Original Article
, Volume: 14( 4)Bioremediation-An Effective Cleanup Technology
- *Correspondence:
- Nida TK , Department of Biotechnology, Faculty of Life Sciences and Informatics, Balochistan University of Information Technology Engineering and Management Science,(BUITEMS), Quetta, Pakistan, Tel: 03368164903; E-Mail: nidatabassumkhan@yahoo.com
Received: June 11, 2018; Accepted: June 14, 2018; Published: June 21, 2018
Citation: Khan NT. Bioremediation-An Effective Cleanup Technology. Environ Sci Ind J. 2018;14(4):170
Abstract
Bioremediation is a technology in which microorganisms, such as bacteria, fungi, protists and yeast are used to degrade harmful substances into non-toxic or less toxic substances to solve environmental problem. It is a waste management technique in which living organism are used to clean up pollution by removing or neutralizing pollutants from contaminated sites or to break down hazardous substances into less toxic or nontoxic forms by using naturally occurring bio-components. There are different natural contamination processes that occur for substance breakdown. When waste is bio-remediated it can be recycled, or at least, stored in such a way that it causes no further harm to the environment around it. Bioremediation is one of the cost effective and safest methods we have now to degrade contaminated waste. Which bioremediation approach is taken relies on the type(s) of microorganisms officially displaying at the pollution site. For instance, if the microorganisms effectively introduced are proper to separate the kind of pollution, cleanup groups may just need to "nourish" these microorganisms by the expansion of composts, supplements, oxygen, phosphorus, and so on. Keywords
Keywords
Biostimulation; Biopile system; Bioventing; Composting; Mycoremediation
Introduction
Bioremediation is a practice where microorganisms are used for removing contaminants by converting it into nontoxic forms which are less harmful for the environment [1]. Bioremediation is a naturally occurring process in which small living organisms called microbes clean up contaminated soil, ground water and surface [2]. Microbes use contaminants as a source of food and energy by harvesting carbon and energy from the breakdown of pollutants whether in aerobic condition or anaerobic condition [3]. In aerobic condition microbes require oxygen to convert toxic waste into water and carbon dioxide while in anaerobic conditions microbial activity occurs in the absence of oxygen [4]. It is very vital to know that this process for waste remediation uses no toxic chemicals, while it may occur by usage of an organism that can be harmful under certain environments [5]. Bioremediation helps by providing these organisms with many ingredients like fertilizer, oxygen and other circumstances to survive. This would help to break the organic pollutant at a faster rate [6]. This remediation process can help to clean up oil spills as oil spills have adverse effect on some organisms [7]. At spots occupied with waste organic material, microorganisms (fungi or bacteria) at that spot break down organic matter to decompose the waste [8].
Significance of bioremediation
No chemical usage: Usually man-made chemicals were used for waste management which had adverse effects on animals, plants and humans [9]. But now with the applications of bioremediation for waste management such adverse effects have been minimized [10]
Recycling of waste: Bioremediation also favors the recycling of waste. When the waste is treated and the contaminant is removed, the waste itself can then be recycled [11].
Principles of bioremediation
Bioremediation occur through natural processes carried out by microorganisms fungi plants to degrade and detoxify substances that is a threat to other living organisms [12]. The microorganisms may be indigenous to a contaminated area or may be brought from elsewhere to the contaminated site [13]. The transformation of contaminants occurs by living organisms through reaction that take place as a part of their metabolic processes [14]. Biodegradation of a compound is accomplished as a result of action of multiple organisms [15]. The more the environmental conditions are favorable for the growth and activity of microorganisms the more the degradation process occur at faster level [16]
Agents of bioremediation
The interaction of microbes with environment and pollutants is very important in determining the effectiveness of bioremediation process [17]. These microorganisms are either present naturally at the site of bioremediation or isolated from other sites e.g. bacteria (aerobic and anaerobic), fungi, archaea etc [18]
Factors affecting bioremediation process
Microbes require optimal condition for good performance and there are various factors that affects the efficiency of microbial biodegradation including:
pH: pH of the soil is one of the most important factor because microbes only survive to a limited range of pH because it effects the availability of nutrients [19]. Optimal range of pH required is 6.5 to 7.5 [20].
Temperature of soil matrix: Temperature influences enzymatic reactions and thus affects the rate of biodegradation [21]. Enzymatic reactions in a cell is doubled by 10 degrees rise in temperature and there is highest temperature limit that microbes can withstand. For example, mesophilic bacteria can withstand temperature from 25 degrees to 45 degrees. Similarly, thermophilic bacteria is activated when temperature is raised up to 60 degree [22,23].
Moisture content: Water availability affects circulation and movement of nutrient into and out of the microorganism cells [24]. High content of moisture is not good because it decreases availability of oxygen which is necessary for respiration of microbes [25]. 50 to 70 percent of water is required usually [26].
Nutrient availability: Nutrients like oxygen and nitrogen is very important for microbial activity and cell growth. For example, treating nitrogen with petroleum contaminated soil increase the growth of cells, decreases microbial lag phase and helps to maintain microbe population and increases hydrocarbon degradation [27].
Approaches of bioremediation
Natural bioremediation: It includes degradation of dead vegetation and dead animals which is a part of carbon, nitrogen and sulfur cycle [28]. Microorganisms uses the chemical energy that is present in the waste material for their growth by converting it into water and CO2 [29].
Managed bioremediation: Application of bioremediation by humans is said to be managed [30]. For example managed biodegradation of organic compounds i.e. land farming. Many petroleum companies uses this process where high molecular weighted organic compounds are spread on to the soil and tilled into the ground with the help of fertilizers [31].
Types of bioremediation
1. In- Situ bioremediation
2. Ex-Situ bioremediation
In-situ bioremediation: In-situ means to neutralize the contaminant at the place of its origin when contaminants are treated at its occurrence site instead of removing the contaminant and treating it elsewhere [32]. In this way it prevents the spread of contamination during displacement and transport [33]. For example to clean up contaminated groundwater in- situ, wells are drilled to pump some of the groundwater into tanks that are present above the ground. Here, the water is purified through microbes and is then pumped back into the ground [34]. The main advantage of in-situ treatment is that it inexpensive and poses minimum harm to the surrounding biome [35]. Microorganisms can also be hereditarily designed to corrupt particular contaminants. A case of microorganism that has been hereditarily designed is Pseudomonas fluorescence HK44. These hereditarily built microorganisms can be intended for the conditions at the site [36].
There are two types of in-situ bioremediation named as intrinsic bioremediation and engineered bioremediation [37]
Intrinsic bioremediation: It is bioremediation under natural condition. This treatment uses microbes that are already present in environment to degrade contaminants and pollutants. No human intervention is involved and is the cheapest commonly used method [38].
Engineered bioremediation: In this type of treatment, engineered microbes are introduced at the site of contamination to accelerate the degradation process [39].
Methods of in-situ Bioremediation
Bioventing
It involves the supply of air and nutrients to the contaminated soil to stimulate local microbes to perform biodegradation. It can be successfully useful for the compounds ranging from gasoline to heavier hydrocarbons. The availability of oxygen enhances the rate at which aerobic bioremediation takes place [40].
Biosparging
It involves the injection of air at pressure below the water table to increase groundwater oxygen concentration and enhances the rate of biological degradation by naturally occurring microbes [41].
Bioaugmentation
This practice involves the addition of specialized microbes and enzymes to the polluted sites to accelerate the transformation or stabilization of specific pollutants [42].
Bio-stimulation
It is a type of bioremediation in which nutrients are added to the polluted area to increase the growth or population of waste degrading microorganism. It also involves the optimization of environmental conditions such as aeration or adding nutrients. Advantage of bio-stimulation is that it deals with microorganisms that are naturally suitable for the environment [43].
Metal biosorption/bioleaching
It is the process in which metals are dissolved by using microorganisms. Some bacteria produce enzymes that cause oxidation of metal ores to release more soluble form of minerals. Certain fungi are able to extract gold by bioleaching [44].
Hydrogen peroxide injection
In cases in which the defilement has just come to the groundwater, bioventing won't be exceptionally fruitful. Rather, hydrogen peroxide is utilized. It works much the same as bioventing, utilizing the hydrogen peroxide rather than air blowers to convey oxygen to the microorganisms. In the event that the dirt is shallow (the groundwater is genuinely near the surface) the hydrogen peroxide can be controlled through sprinkler frameworks. On the off chance that the groundwater is genuinely far below the surface, infusion wells are utilized [45,46].
Ex-situ bioremediation: This type of remediation treatment occurs after contaminated waste has been removed and transported to the area where it is treated [47]. At the sites where temperature is low to the point where microbes become inactive or the soil is excessively dense because of which the nutrients cannot spread evenly underground. At such sites ex situ bioremediation is used which means that the process is conducted outside of the location [48]. Ex- situ bioremediation is much effective than in -situ as it is less time consuming and can be used against wide range of contaminants. Moreover in ex-situ procedure the nutrients added to the soil or water are more evenly distributed because of homogenizing and mixing the polluted medium in a bioreactor [49]. However, the increased transport costs, additional land requirement and higher levels of engineering makes ex-situ remediation a more costly option. Another problem that is associated with ex-situ method is that during digging or pumping of contaminated soil or groundwater the contaminants may release in the environment if not managed properly [50].
Methods of ex-situ bioremediation
Composting: it is the addition of nutrients to soil to increase the rate of aeration and activation of native microorganisms. Organic matter formed from composting benefits in improving soil quality. It takes place in a distinct container, when composting is done then it is fused into the soil. This method is cost-effective technique for soil bioremediation and is done on both large and small scales. It can be used for organic pollutants and other type of wastes depending on the adsorption competences of organic matter and microbes degradation abilities [51].
Landfarming: It is the technique in which contaminated soil is taken and spread out on a prepared bed and tilled periodically until pollutants are degraded. But this process is limited to treatment of soil up to 10-35 cm [52].
Biopile system: It is a hybrid of land farming and composting. It is used for the treatment of surface contaminants with petroleum hydrocarbons. It provides favorable environment for aerobic and anaerobic microorganisms Exhumed soils are added with soil adjustments and their product is placed on treatment area. This type is helpful for oil and hydrocarbon waste. The remediated soil is then placed in insert to prevent more contamination of the soil. Bio-piles have perforated pipes to optimize air and blowers to optimize the supply of oxygen, which further help for other factors such as pH [53,54].
Bioreactors: Slurry reactors or aqueous reactor are used for ex-situ treatment of contaminated soil and water pumped up from contaminated plume. It involves the treatment of contamination through engineered contamination system [55].
Uses of bioremediation includes
1. Soil bioremediation
2. Waste water treatment
3. Biodegradation of hydrocarbons
4. Biotreatment of gaseous streams
5. Soil waste bioremediation
Types of Bioremediation based on microbial agents
Phytoremediation: Removal of contamination by the use of plants. Plants have the potential to draw the contaminants such as petroleum, hydrocarbons, metals, chlorinated solvents etc. into their structures and hold on to them [59]. It is an efficient way to remove contaminants from soil and water. For example Indian mustard is really useful to accumulate certain metals like cadmium, lead and selenium. Poplar tree on the other hand can degrade petroleum hydrocarbons like benzene and toluene [60,61].
Stages of phytoremediation
Phytoextraction: This process include the uptake of substances from the environment and their accumulation in the plants [62].
Phytostabilization: Limit the transfer and movement of substances in to the environment i.e. limits the leaching of contaminants [63].
Phytotransformation: When the plants uptake the substance from environment and the plants degrade it in its own body [64].
Phytovolatilization: It is the removal of contaminants from soil and water and then releasing it into the air [65].
Rhizofiltration: It is the removal of toxic from ground water through root activity i.e. in the rhizosphere it is usually used to disinfect groundwater. Plants are grown in greenhouses in water instead of soil. These plants are then planted on the site of contaminated groundwater where the roots take up the water and contaminants. Once the roots are saturated with the contaminant, the plants are gathered including the roots. In some countries sunflowers are used to remove radioactive contaminants from groundwater by rhizofiltration [66].
Mycoremediation: Fungi’s digestive enzyme used to degrade contaminants such as hydrocarbons, heavy metals and pesticides [67].
Advantages of bioremediation
1. Natural process therefore perceived by public
2. Complete destruction of contaminants
3. It can be carried out on original sites without disrupting normal activities
4. It is less expensive and less disturbing to the environment
5. Unlike other remediation technologies bioremediation detoxifies harmful substances instead of only transferring them from one place to another
6. Byproducts of bioremediation are usually water and carbon dioxide which are less harmful to the environment as compare to the end results of conventional methods of waste treatment
7. The byproducts of bioremediation can usually be converted into some other useful substance such as humus
8. Less technology and supervision is required [68-71].
Disadvantages of bioremediation
1. It is time consuming process and cannot remove all kind of contaminants
2. In-situ bioremediation is not effective if the soil is very dense and has low permeability
3. Limited to those compounds that are biodegradable only. All compounds are not being completely degradable
4. The end product may come out more toxic than parent compound
5. Process is highly specific means optimal temperature, pH, suitable environment and different nutrients are needed
6. Time consuming process and difficult to control volatile substances through ex-situ remediation method [72-76]
Conclusion
Plants, microbes and other organisms can be used for the prevention and cleanup of environmental pollutants with the advent of new technologies. Researches are now able to stabilize, degrade and breakdown contaminants to useful products by using natural processes that is reliable, inexpensive and more productive. It is imperative to comprehend that this type of waste remediation utilizes no lethal chemicals, despite the fact that it might utilize a creature that can be hurtful in specific situations.
References
- Baker KH, Herson DS. Bioremediation. McGraw-Hill, Inc.; 1994.
- Vidali M. Bioremediation: An overview. Pure Appl. Chem. 2001;73(7):1163-72.
- Cookson Jr JT. Bioremediation engineering: Design and application. McGraw-Hill, Inc.; 1995.
- Abramowicz DA. Aerobic and anaerobic biodegradation of PCBs: A review. Crit Rev Biotechnol. 1990;10(3):241-51.
- Rajendran P, Muthukrishnan J, Gunasekaran P. Microbes in heavy metal remediation.2003
- Lovley DR, Coates JD. Bioremediation of metal contamination. Curr Opin Biotechnol. 1997;8(3):285-9.
- Hawkins, A. Bioremediation of Oil Spills.
- Gadd GM. Metals, minerals and microbes: Geomicrobiology and bioremediation. Microbiol.2010;156(3):609-43.
- Megharaj M, Ramakrishnan B, Venkateswarlu K, et al. Bioremediation approaches for organic pollutants: A critical perspective. Environ Int. 2011;37(8):1362-75.
- Gavrilescu M. Environmental biotechnology: Achievements, opportunities and challenges. Dynamic biochemistry, process biotechnology and molecular biology. 2010;4(1):1-36.
- Scragg AH. Environmental biotechnology. New York: OXFORD university press; 2005.
- Eweis JB, Ergas SJ, Chang DP, et al. Bioremediation principles. McGraw-Hill Book Company Europe; 1998.
- Sylvia DM, Fuhrmann JJ, Hartel PG, et al, Editors. Principles and applications of soil microbiology. Upper Saddle River, NJ: Pearson Prentice Hall; 2005.
- Council N. In Situ Bioremediation; When Does it Work.1993.
- Alexander M. Biodegradation and bioremediation. Gulf Professional Publishing; 1999.
- Hatzikioseyian A. Principles of bioremediation processes. Trends in Bioremediation and Phytoremediation. India: Research Signpost. 2010.
- Pieper DH, Reineke W. Engineering bacteria for bioremediation. Curr Opin Biotechnol. 2000;11(3):262-70.
- Watanabe K. Microorganisms relevant to bioremediation. Curr Opin in Biotechnol. 2001;12(3):237-41.
- Gavrilescu M. Removal of heavy metals from the environment by biosorption. Engineering in Life Sciences. 2004;4(3):219-32.
- Tyagi M, da Fonseca MM, de Carvalho CC. Bioaugmentation and biostimulation strategies to improve the effectiveness of bioremediation processes. Biodegradation. 2011;22(2):231-41.
- Margesin R, Schinner F. Biodegradation and bioremediation of hydrocarbons in extreme environments. Appl Microbiol Biotechnol. 2001;56(5,6):650-63.
- Chibuike GU, Obiora SC. Heavy metal polluted soils: Effect on plants and bioremediation methods. Appl Environ Soil Sci.2014.
- Polymenakou PN, Stephanou EG. Effect of temperature and additional carbon sources on phenol degradation by an indigenous soil Pseudomonad. Biodegradation.2005;16(5):403-13.
- Boopathy R. Factors limiting bioremediation technologies. Bioresour Technol.2000;74(1):63-7.
- Huesemann MH, Truex MJ. The role of oxygen diffusion in passive bioremediation of petroleum contaminated soils. J Hazard Mater.1996;51(1-3):93-113.
- Kosaric N. Biosurfactants and their application for soil bioremediation. Food Technol Biotechnol. 2001;39(4):295-304.
- Park JH, Lamb D, Paneerselvam P, et al. Role of organic amendments on enhanced bioremediation of heavy metal (loid) contaminated soils. J Hazar Mater. 2011;185(2-3):549-74.
- Ruberto L, Vazquez SC, Mac Cormack WP. Effectiveness of the natural bacterial flora, biostimulation and bioaugmentation on the bioremediation of a hydrocarbon contaminated Antarctic soil. Int Biodeterior Biodegradation. 2003;52(2):115-25.
- Scow KM, Hicks KA. Natural attenuation and enhanced bioremediation of organic contaminants in groundwater. Curr Opin Biotechnol. 2005;16(3):246-53.
- Ripp S, Nivens DE, Ahn Y, et al. Controlled field release of a bioluminescent genetically engineered microorganism for bioremediation process monitoring and control. Environ Sci Technol. 2000;34(5):846-53.
- Duncan K, Levetin E, Wells H, et al. Managed bioremediation of soil contaminated with crude oil soil chemistry and microbial ecology three years later. Appl Biochem Biotechnol. 1997;63(1):879-89.
- Rittmann BE, Seagren E, Wrenn BA. In situ bioremediation. Taylor & Francis; 1994.
- Council N. In Situ Bioremediation; When Does it Work.1993.
- Romantschuk M, Sarand I, Petänen T, et al. Means to improve the effect of in situ bioremediation of contaminated soil: an overview of novel approaches. Environ Pollut. 2000;107(2):179-85.
- Pandey J, Chauhan A, Jain RK. Integrative approaches for assessing the ecological sustainability of in situ bioremediation. FEMS Microbiol Rev. 2009;33(2):324-75.
- Samanta SK, Singh OV, Jain RK. Polycyclic aromatic hydrocarbons: Environmental pollution and bioremediation. Trends Biotechnol. 2002;20(6):243-8.
- Macdonald JA, Rittmann BE. Performance standards for in situ bioremediation. Environ Sci Technol. 1993;27(10):1974-9.
- Hinchee RE, Wilson JT, Downey DC. Intrinsic bioremediation. Battelle, Columbus, OH (United States). 1995.
- Hart S. Peer Reviewed: In Situ Bioremediation: Defining the Limits. Environ Sci Technol. 1996;30(9):398A-401A.
- Hoeppel RE, Hinchee RE, Arthur MF. Bioventing soils contaminated with petroleum hydrocarbons. J Ind Microbiol. 1991;8(3):141-6.
- Johnson PC, Johnson RL, Bruce CL, Leeson A. Advances in in situ air sparging/biosparging. Bioremediation Journal. 2001;5(4):251-66.
- El Fantroussi S, Agathos SN. Is bioaugmentation a feasible strategy for pollutant removal and site remediation?. Curr Opin Microbio. 2005;8(3):268-75.
- Seklemova E, Pavlova A, Kovacheva K. Biostimulation-based bioremediation of diesel fuel: Field demonstration. Biodegradation. 2001;12(5):311-6.
- Siddiquee S, Rovina K, Azad SA, et al. Heavy metal contaminants removal from wastewater using the potential filamentous fungi biomass: a review. J Microb Biochem Technol. 2015;7(6).
- Watts RJ, Foget MK, Kong SH, Teel AL. Hydrogen peroxide decomposition in model subsurface systems. J Hazard Mater. 1999;69(2):229-43.
- Brown RA, Norris RD. The evolution of a technology: Hydrogen peroxide in in situ bioremediation. Hydrocarbon Bioremediation. 1994:148-62.
- Lin TC, Pan PT, Cheng SS. Ex situ bioremediation of oil-contaminated soil. J Hazard Mater. 2010;176(1-3):27-34.
- Tomei MC, Daugulis AJ. Ex situ bioremediation of contaminated soils: an overview of conventional and innovative technologies. Crit Rev Environ Sci Technol. 2013;43(20):2107-39.
- Larsen SB, Karakashev D, Angelidaki I, et al. Ex-situ bioremediation of polycyclic aromatic hydrocarbons in sewage sludge. J Hazard Mater. 2009;164(2-3):1568-72.
- Pavel LV, Gavrilescu M. Overview of Ex situ decontamination techniques for soil cleanup. ENVIRON ENG MANAG J (EEMJ). 2008;7(6).
- Semple KT, Reid BJ, Fermor TR. Impact of composting strategies on the treatment of soils contaminated with organic pollutants. Environ Pollut. 2001;112(2):269-83.
- Maila MP, Cloete TE. Bioremediation of petroleum hydrocarbons through landfarming: Are simplicity and cost-effectiveness the only advantages? Reviews in Environmental science and bio/Technology. 2004 ;3(4):349-60.
- Shukla KP, Singh NK, Sharma S. Bioremediation: Developments, current practices and perspectives. Genet Eng Biotechnol J. 2010;3:1-20.
- Robles-González IV, Fava F, Poggi-Varaldo HM. A review on slurry bioreactors for bioremediation of soils and sediments. Microb Cell Fact. 2008;7(1):5.
- Lynch JM, Moffat AJ. Bioremediation-prospects for the future application of innovative applied biological research. Ann Appl Biol. 2005;146(2):217-21.
- Kumar A, Bisht BS, Joshi VD, et al. Review on bioremediation of polluted environment:A management tool. Int J Environ Sci. 2011;1(6):1079.
- Sharma S. Bioremediation: features, strategies and applications. Asian Journal of Pharmacy and Life Science ISSN. 2012;2231:4423.
- Atlas R. The scope of bioremediation. InBioremediation: The Tokyo ?94 Workshop, Tokyo, Japan 1994.
- Lü JC, Li ZT, Hussain K, et al. Bioremediation: The new directions of oil spill cleanup. Middle-East J Sci Res. 2011;7(5):738-40.
- Salt DE, Smith RD, Raskin I. Phytoremediation. Annu Rev Plant Biol. 1998;49(1):643-68.
- Cunningham SD, Ow DW. Promises and prospects of phytoremediation. Plant Physiol. 1996 ;110(3):715.
- Lasat MM. Phytoextraction of toxic metals. J Environ Qual. 2002;31(1):109-20.
- Schnoor JL. Phytostabilization of metals using hybrid poplar trees. Phytoremediation of toxic metals: using plants to clean-up the environment. New York, John Wiley & Sons, Inc. 2000:133-50.
- McCutcheon SC, Schnoor JL. Overview of phytotransformation and control of wastes. Phytoremediation: Transformation and control of contaminants. 2003;358.
- Baeder-Bederski-Anteda, O. (2003). Phytovolatilisation of organic chemicals. J Soils Sediments, 3(2), 65-71.
- Dushenkov V, Kumar PN, Motto H, et al. Rhizofiltration: the use of plants to remove heavy metals from aqueous streams. Environ Sci Technol. 1995;29(5):1239-45.
- Singh H. Mycoremediation: Fungal bioremediation. John Wiley & Sons; 2006.
- Megharaj M, Ramakrishnan B, Venkateswarlu K, et al. Bioremediation approaches for organic pollutants: a critical perspective. Environ Int. 2011;37(8):1362-75.
- Wang Q, Zhang S, Li Y, et al. Potential approaches to improving biodegradation of hydrocarbons for bioremediation of crude oil pollution. J Environ Prot. 2011;2(01):47.
- Caplan JA. The worldwide bioremediation industry: Prospects for profit. Trends Biotechnol. 1993;11(8):320-3.
- Chowdhury S, Bala NN, Dhauria P. Bioremediation-A natural way for cleaner environment. International Journal of Pharmaceutical, Chemical and Biological Sciences. 2012;2(4):600-11.
- Boopathy R. Factors limiting bioremediation technologies. Bioresour Technol. 2000;74(1):63-7.
- Kang JW. Removing environmental organic pollutants with bioremediation and phytoremediation. Biotechnology Lett. 2014;36(6):1129-39.
- Davison J. Risk mitigation of genetically modified bacteria and plants designed for bioremediation. J Ind Microbio and Biotechnol. 2005;32(11,12):639-50.
- Piotrowski MR, Kostecki PT, Calabrese EJ. Bioremediation of hydrocarbon contaminated surface water, groundwater, and soils: The microbiol ecology approach. Hydrocarbon contaminated soils and groundwater: Analysis, fate, environmental, and public health effects. 1991:203-38.
- Gnanasalomi VD, Jebapriya GR, Gnanadoss JJ. Bioremediation of hazardous pollutants using fungi. Int J Comput Algorithm. 2013;2:273-8.