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© 2018 IJRAR December 2018, Volume 5, Issue 4 www.ijrar.org (E-ISSN 2348-1269, P- ISSN 2349-5138) IJRAR1BIP134 International Journal of Research and Analytical Reviews (IJRAR) www.ijrar.org 778 Effectiveness of Bioremediation for the removal of toxic Heavy Metals Using Microorganisms Bashir Ahmad Aliyu 1 , Nishi Nidhi 1 , Maryam Musa Qaraye 3 , Adamu Muhammad Fagge 4, Arvind Kumar 1 * 1 Department of Biochemistry, School of Bioengineering and Bioscience, Lovely Professional University, GT Road, Phagwara, Punjab, India-144411 2 Department of Biology, School of Science Education, Sa’adatu Rimi College of Education, Kumbotso, P.M.B 3218, Kano State, Nigeria 3 Department of integrated science, School of Science Education, Sa’adatu Rimi College of Education, Kumbotso, P.M.B 3218, Kano State, Nigeria Abstract Bioremediation is an effective technique used to convert toxic heavy metal ions into less harmful compounds, using resistant microorganisms for cleaning the soil and water bodies with heavy metal contamination. Such contaminants are released as a result of indiscriminate use of the natural recourses for human purposes which altered the geochemical cycles and biochemical balance of the ecosystem affecting the human health and aquatic biota. This study will focus on the development of good efficient, eco-friendly and cost-effective method for the remediation of inorganic metals like Pb, Cr, Cd, and Hg that are released into the environment and the safeguard measures by using recent advances in bioremediation using microbes linked to heavy metal degradation. It will emphasis the use of bioremediation as a prospective techniques in an ecosystem due to their nature of non-biodegradability that could be toxic to microorganisms, a specific technique for the efficient removal of contaminants to be achieved using different mechanism by identifying the microbes that are resistant to heavy metal ions. However, this review will focused on the use of bacteria, fungi, algae and other microbes that shows a synergic and bio-sorption capacity effect for removal of heavy metals ions in an environment. Key words: Bioremediation, Microorganisms, Toxicity, Heavy metal ions

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  • © 2018 IJRAR December 2018, Volume 5, Issue 4 www.ijrar.org (E-ISSN 2348-1269, P- ISSN 2349-5138)

    IJRAR1BIP134 International Journal of Research and Analytical Reviews (IJRAR) www.ijrar.org 778

    Effectiveness of Bioremediation for the removal of

    toxic Heavy Metals Using Microorganisms

    Bashir Ahmad Aliyu1, Nishi Nidhi1, Maryam Musa Qaraye3, Adamu Muhammad Fagge4,

    Arvind Kumar1*

    1Department of Biochemistry, School of Bioengineering and Bioscience,

    Lovely Professional University, GT Road, Phagwara, Punjab, India-144411

    2Department of Biology, School of Science Education,

    Sa’adatu Rimi College of Education, Kumbotso, P.M.B 3218, Kano State, Nigeria

    3Department of integrated science, School of Science Education,

    Sa’adatu Rimi College of Education, Kumbotso, P.M.B 3218, Kano State, Nigeria

    Abstract

    Bioremediation is an effective technique used to convert toxic heavy metal ions into less harmful compounds, using

    resistant microorganisms for cleaning the soil and water bodies with heavy metal contamination. Such contaminants

    are released as a result of indiscriminate use of the natural recourses for human purposes which altered the

    geochemical cycles and biochemical balance of the ecosystem affecting the human health and aquatic biota. This

    study will focus on the development of good efficient, eco-friendly and cost-effective method for the remediation of

    inorganic metals like Pb, Cr, Cd, and Hg that are released into the environment and the safeguard measures by using

    recent advances in bioremediation using microbes linked to heavy metal degradation. It will emphasis the use of

    bioremediation as a prospective techniques in an ecosystem due to their nature of non-biodegradability that could be

    toxic to microorganisms, a specific technique for the efficient removal of contaminants to be achieved using different

    mechanism by identifying the microbes that are resistant to heavy metal ions. However, this review will focused on

    the use of bacteria, fungi, algae and other microbes that shows a synergic and bio-sorption capacity effect for removal

    of heavy metals ions in an environment.

    Key words: Bioremediation, Microorganisms, Toxicity, Heavy metal ions

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    Introduction

    Bioremediation is a new biological technique used for recycling wastes and reduce their toxicity into less toxic form,

    microorganisms that are widely distributed on the biosphere due to their metabolic ability can easily grow in a wide

    range of environmental conditions affected with heavy metals ions contaminat. The use of bioremediation as a

    biotechnological process, involves the use of microorganisms to reduced environmental pollutants through

    biodegradation process. The effectiveness of Bioremediation and biodegradation apply the use of microorganisms

    that act as a significant pollutant removal tools in soil, water, and sediments using remediation routine

    protocols. According to research by (Zakharova & Gussman, 1997), describe Bioremediation as a novel

    technique used to reduced environmental contaminants from the habitat, and utilizes the biological inherent of

    microbes and plants to eradicate toxic pollutants and restore the originality of environmental flora. One of the basic

    principles of bioremediation technique involve reducing the solubility of environmental contaminants, by changing

    the pH, redox reactions and adsorption of contaminants from polluted environment were microorganisms

    are restoring the original and natural surroundings by preventing further pollution (Demnerová et al., 2005).

    However, the presence of microorganisms of the environment keeps on decreasing the rate of

    environmental contamination due to the anthrophogenic activities of both domestic, Agricultural and industry by

    human which degrades and affect the environmental condition. The heavy metals ions contaminants that spill

    out into the environment are persistent to thos, heavty metals ions and led to a severe threat to organisms that are

    not resistant and exposed them to high levels enviromenal contamination. Toxic heavy metals ions such as lead,

    cadmium, mercury, chromium, zinc, uranium, selenium, silver, gold, nickel and arsenic, that are not useful to

    plants, are capable of reducing plant growth by photosynthetic activities as well as reducing the activity

    of essential enzymes (Nematian & Kazemeini, 2013). A resaerch suggest that bioremediation is an alternative

    way used to abstract a toxic contaminants from waste effluents release into the environmental by human

    activities using super bug in cleaning up oil spills to decrease the toxicity of metals ions by minimising the

    environmental contaminant using microcroorganisms as remediation process (Mohan & Dubey, 2013). In general

    Metals are natural constituents of earth such as; Zn, Ni, Cu that are essential for living organisms, but prove

    toxic to micro and macro organisms at higher concentrations of heavy metals ions. The presence of Lead, cadmium

    and mercury are toxic to bacterial cells as such affect environmental flora even at low concentrations due

    to their toxicity (Microbiology, Microbiology, & Avenue, 1995). Current rapid industrialization, heavy metals

    have accumulated over several decades and require special attention to be treated into less toxic, wastes from

    mining, metal refining industries, sewage sludge, power plant and waste incineration plants, contain high levels

    of Pb, Hg and Cd which create serious detriment to environmental biota and urgently need to be removed

    from environmental. As cited by (Lovley & Coatest, n.d.), microorganisms for environmental restoration have

    focused primarily on microbial degradation of organic contaminants. There has been little investigation regarding

    microorganisms used for remediation of heavy metal ions contamination whereby microorganisms destroy organic

    effluent by oxidizing them to carbon dioxide and alter the evolutionary of metal contaminants. According to

    (Jin & Luan, 2018), microorganisms can remove toxic heavy metals ions contaminants and metalloids from

    contaminated water and waste streams by converting them into

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    volatilized form. The management of heavy metal ions in soil using microorganisms relies on therapeutic ecological

    restoration methods based on adsorption and transfer process. Chemical methods usually involve direct reactions

    between chemical reagents and heavy metal ions, such as chelation and redox, while chemical restoration methods

    are often promoted by other methods, such as electrochemical repair (Race, 2017). Subsequently, the microorganisms

    with distinctive features of catabolic potential like enzymes and bio surfactant is a novel approach to enhance and

    boost efficacy of microbes in the environment. However, different alternatives may likely widen the microbiological

    application towards remediating heavy metals ions contamination, the use of microbes to degrade recalcitrant heavy

    metals has been explored using biofilm mediated bioremediation that can be applied for cleaning up of heavy metal

    contaminated site (Igiri et al., 2018). According to (Gupta et al., 2016), heavy metal contaminants affect populace

    who live near the polluted sites, and are frequently found normally in soil, sediments and water. The excessive

    Breathing, eating, drinking, and skin interaction are all likely exposure routes for metal contaminants, and affect the

    function of kidneys, mental capabilities, weakness, headaches, abdominal cramps and anemia due to Chronic contact

    with contaminated heavy metal ions, and result in permanent kidney and brain damage (Ayu, Hadibarata, Toyama,

    Tanaka, & Mori, 2011), as such metal like cadmium is tremendously toxic and was shown to denature the DNA

    helical structure. The use of microorganisms for industrial sewages treatment of contaminated sites, of metal with

    high concentrations in the activated sludge that execute various health problems like headache, irritability, abdominal

    pain and numerous symptoms associated to the nervous system, anxiety, bladder and kidney cancer either by indirect

    transfer of vital nutritional minerals from their original place, thus, affecting their biological function and accumulate

    in the body, as well as affecting the organs and glands, whereby the microorganisms have altered the heavy metals

    and become metal resistant.

    In this review, several research in the past two decades, that shows effectiveness and modern advances in

    bioremediation techniques that restore environmental contamination using an eco-friendly approach at a very low

    cost, The theme have developed and bring different bioremediation techniques but due to nature there is no single

    bioremediation technique that restore the contamination as at that time, but Autochthonous (indigenous)

    microorganisms present in polluted environments play an important role in solving most of the challenges associated

    with biodegradation and bioremediation of heavy metal ions contamination (Jaiswal, Verma, & Jaiswal, 2018), thus,

    provide an effective environmental conditions suitable for their growth and metabolism, eco-friendly and cost saving

    features of bioremediation compared to both chemical and physical methods of remediation (Chibueze, Chioma, &

    Chikere, 2016).

    Microorganisms used in bioremediation

    The use of Microbes have develop diverse approaches to prevail the toxic effects of metals and metalloids, by

    utilizing their accumulation, resistance or by reducing their toxicity into less toxic form through biomethylation and

    transformation. The higher concentrations of heavy metals have been predictable as an environmental treat in aquatic

    and environmental ecosystems all over the world. Several of these heavy metals reach ground water as a result of

    unwanted human activity and other factors that accumulate in seafood and plants (Dobson & Burgess, 2007). The

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    heavy metals uptake by microorganisms or passively by microbial cell walls that mainly consist of polysaccharides,

    lipids and proteins, provide numerous functional groups that will bind to heavy metal ions, such as carboxylate,

    hydroxyl, amino and phosphate groups (Dixit et al., 2015). Moreover, various microorganisms that enhance the

    methods of biosorption process seem to be more effective for large scale application compared to the

    bioaccumulation process, microbes require addition of specific amount of nutrients for their lively uptake of heavy

    metals ions and increases their biological oxygen demand/chemical oxygen demand in the contaminated

    environment. Furthermore, the need of maintaining healthy population of microbes due to its nature of toxicity and

    other environmental factors (Britain, 1998). But Fungi, Penicillium, Aspergillus and Rhizopus have been studied

    extensively to serve as potential microbial agents for the removal of heavy metals in an environment. The character of

    microbes and their high metabolic diversity and adaptability have high tendency to survive in the most diverse natural

    and artificial environment as a result of environmental contamination and become resistant heavy metals ions.

    Consequently, different microbes can be use in an ex and in situ bioremediation and reducing the toxicity of the

    environment into less toxic form. However, microbes that live in an intensely competitive environment, has to

    develop certain resistant device, to colonize the ecological habitat and metabolize common nutrients quickly, or use

    nutrients that favour the microbes. While in non competitive environments with extreme conditions of temperature,

    salinity, acidity, etc., microbes need special physiological characteristics, which provide good favorable life

    condition, while Some microorganisms can use other means, such as the production of acids and antibiotics (Iranzo,

    Boluda, & Sánchez, 2001).

    The presence of natural sources or due to human activities, heavy metal ions are found in surface water, wastewater,

    waste and soils, by given proper potential health hazard to heavy metals that affect the system of our environmental

    flora, as most industries use heavy metals in one way or the other due to their technological importance and

    applications, such as metal processing, electroplating, electronics and chemical processing industries. Furthermore,

    the presence of heavy metal ions will be control using approved and specific microbes before they are released, for

    environmental safety, because the treatment of the contaminated environmental sites is of great concern since heavy

    metal ions accumulate in living species with a permanent toxic and carcinogenic activity (Dixit et al., 2015). Though,

    sometimes the common treatment processes include chemical precipitation, oxidation/reduction, ion exchange,

    membrane technologies, reverse osmosis, and solvent extraction. Though each process has limitation and delimitation

    as well as application on the heavy metal ion concentration (Aly, Alzahrani, Amashah, & Jastaniah, 2018). But the

    various human anthropogenic activities as a result of agriculture, fishing and industry, produce abnormal

    accumulation of different materials in the environment, although most of the contaminants are biodegradable,

    containing mostly natural organic matter (agriculture or animal residues). Sometimes, the high quantity of production

    render it impossible to eliminate them in short periods of time with other natural organic substance, such as oils or

    petroleum hydrocarbons that could be degraded easily. Moreover, the improper industrial activities produce many

    toxic chemicals that are not present in nature, such as plastics, pesticides, and enter the ecosystems in large amounts

    and affect the biodegradation process.

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    Sources of heavy metals

    The excessive release of Rural and Urban contamination is a worldwide and affect environmental flora, human health

    as well as affecting our environmental micro biota that mostly affect rapid growing cities in developing countries,

    such as China that strongly affected by anthropogenic activity by human and indicate highest burden of diseases

    (Cohen et al., 2004; Chen et al., 2011). However, according to World Health Organization (WHO) estimated that

    annually almost 300,000 people rashly die due to urban release contaminants in China and less number in India, the

    atmospheric contaminant of heavy metals can impose a long term burden on biogeochemical cycling in the ecological

    ecosystem (Kelly et al., 1996; Nriagu, 1988; Nriagu and Pacyna, 1988). More so, the chemical release include; As,

    Cr, Ni, Pb, Zn, Cu and Cd are carcinogenic and As and Cd are potentially mutagenic, Pb and Hg are fetal toxic

    respectively (Cheng, 2003; He et al., 2001). In recent years, research shows that the heavy metal contaminants have

    been reported frequently in China and microbes are the prior consideration given for their vital role in environmental

    treatments (Zhou, 2011). However, as a result of high number of causalities recorded, in February 2011, the State

    Council officially approved the “12th Five-Year Plan” for comprehensive prevention and control of heavy metals

    pollution release in to environment (Duan, Tan, Hao, & Chai, 2016). Mostly, the sources of such contaminants are

    released as illustrated in the chat below;

    Anthropogenic sources of heavy metals ions caused by Humans activities

    Effects of Heavy Metals in an Environment

    The presence of non biodegradability nature of toxic heavy metals ions makes it hard to be remove from using

    biological tissues in contaminated environment, thus, is a major concern of global health due to fatal nature of

    environmental contamination due to the presence of cobalt, copper, iron, manganese and molybdenum that are

    required in small quantities for the survival of microorganisms as well as nature of higher concentrations and become

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    detrimental to heavy metals, such as; Hg, Cr, As, Zn, Cd, Au and Ni that are hazardous and rapidly contaminate the

    environment as well as affecting the quality of the soil, crop production. Consequently, if the toxicity exceeds the

    maximum permissible concentration in water given by the Comprehensive Environmental Response Compensation

    and Liability Act by USA: Ar (0.01 mg·L−1), Cd (0.05 mg·L−1), Cr (0.01 mg·L−1), Pb (0.015 mg·L−1 ), Hg (0.002

    mg·L−1 ) and Ag (0.05 mg·L-1) respectively, and become hazardous to human health (Jaiswal et al., 2018). The

    release of contaminant, serve as the major sources of diseases and affect humans life such as cancer, Alzheimer’s

    disease, atherosclerosis and Parkinson’s disease due to their high level toxicity of each metal that determined by the

    duration of exposure as well as the absorbed dosage by an organisms, and affect the high metal toxicity that inhibits

    by cytoplasmic enzymes in plant cells and causes damage to cell structures due to oxidative stress and consequently

    affects plant growth and metabolism (Ojuederie & Babalola, 2017).

    Mechanisms of Bioremediation

    Heavy metals are known to remove important components in biological molecules and hindering the functions of the

    microbes by changing the enzymatic function, protein or membrane transporter structure, thereby accumulate in the

    plants tissue, the use of resistant microorganisms can be apply for the treatment of such toxic heavy metal

    degradation. And also another efficient way used for the removal of contaminants in an environment by stabilizing

    the ecosystem and use the indigenous microorganism capable of degrading such heavy metals, or genetically

    engineered microorganisms to treat polluted environments by converting the toxic heavy metals into less toxic form

    (Nematian & Kazemeini, 2013).

    Figure 2 below shows the major groups of microorganisms commonly used for the bioremediation of metals using

    different microbes

    Fig 2: Microorganisms employed in the bioremediation processes

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    Biotransformation

    Biotransformation are structural modifications in an effective bioremediation by using chemical compound produced

    by an organisms /enzyme systems that lead to the formation of molecules with relatively greater polarity using

    mechanism that has been developed by adapted microbes to an environmental changes of biotechnological processes.

    and maintains the original carbon skeleton. The biotransformation is divided into two types:

    Enzymatic: the enzymatic are further divided into Microsomal and Non-Microsomal and is occurring due to various

    enzymes present in the body

    i- Microsomal biotransformation: is caused by enzymes present within the lipophilic membranes of

    smooth endoplasmic reticulum

    ii- Non-Microsomal Biotransformation: involves the enzymes which are present within the

    mitochondria.

    Non-enzymatic: Is highly active, unstable compounds taking place at physiological pH Some of which include

    Chlorazepate that are converted into Desmethyl diazepam, Mustin HCl and converted into Ethyleneimonium and

    finally into Formaldehyde.

    Biosorption

    Is the search for new technology that involve the use of biological phenomenon to accumulate and detoxify heavy

    metals from wastewater that metabolically mediated or physic chemical system uptake in a solid phase (sorbent or

    biosorbent; biological material) and a liquid phase (solvent, normally water) containing a dissolved species (Fourest

    and Roux, 1992), the presence of Algae, bacteria, fungi and yeasts, have proved to be potential in metal biosorbents

    with advantages over conventional treatment methods that include:

    • Low cost;

    • High efficiency;

    • Minimization of chemical and or biological sludge;

    • No additional nutrient requirement;

    • Regeneration of biosorbent; and

    • Possibility of metal recovery.

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    Bioaccumulation

    Microorganisms used in heavy metal remediation of contaminated sites

    The effectiveness of microorganisms for bioremediation of heavy metals ions is the use of consortium

    microorganisms; the prokaryotes and Eukaryotes microbes develop a natural capacity to biosorb toxic heavy metal

    presents in an environment using microbes such as;

    Bacteria

    Arthrobacter spp., Pseudomonas veronii, Burkholderiaspp, Kocuria flava and Bacillus cereus

    Fungi

    Penicillium canescens, Aspergillus versicolo and Aspergillus fumigatus

    Algae

    Cladophora fascicularis, Spirogyra spp., Cladophora spp., Spirogyra spp. And Spirullina spp.

    Yeast

    Saccharomyces cerevisiae and Candida utilis.

    The way by which microbes interact with heavy metal ions is partially dependent on either eukaryotes or prokaryotes

    whereby several microbes including aerobes, anaerobes, and fungi, are involved in an enzymatic degradation process

    using indigenous microorganisms (Coelho et al., 2015).

    Conclusion

    In conclusion, the natural and anthropogenic actions as a result of domestic and industrial activities produce large

    quantities of aqueous effluents containing toxic heavy metals that are release into the environment and affect its

    microbial flora. However, the use of good efficient, eco-friendly and cost-effective method using consortium

    microorganisms for the remediation of inorganic metals will be very effective and reduce the level of contamination

    in the environments.

    Bioaccumulation is a metabolically an active process where microorganisms uptake heavy metals into their

    intracellular space using importer complexes that create a translocation pathway through the lipid bilayer inside the

    intracellular space, by which the heavy metals will be sequestered by proteins and peptide (Britain, 1998).

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