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Review

Biosorption: An Interplay between Marine Algae and Potentially Toxic Elements—A Review

by
Muhammad Bilal
1,
Tahir Rasheed
2,
Juan Eduardo Sosa-Hernández
3,
Ali Raza
4,
Faran Nabeel
2 and
Hafiz M. N. Iqbal
3,*
1
State Key Laboratory of Microbial Metabolism, School of Life Sciences and Biotechnology, Shanghai Jiao Tong University, Shanghai 200240, China
2
State Key Laboratory of Metal Matrix Composites, The School of Chemistry & Chemical Engineering, Shanghai Jiao Tong University, Shanghai 200240, China
3
Tecnologico de Monterrey, School of Engineering and Sciences, Campus Monterrey, Ave. Eugenio Garza Sada 2501, Monterrey, N.L., CP 64849, Mexico
4
School of Biomedical Engineering, Shanghai Jiao Tong University, Shanghai 200240, China
*
Author to whom correspondence should be addressed.
Mar. Drugs 2018, 16(2), 65; https://doi.org/10.3390/md16020065
Submission received: 22 January 2018 / Revised: 9 February 2018 / Accepted: 16 February 2018 / Published: 19 February 2018
(This article belongs to the Special Issue Marine Compounds Used in Biosorption)
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Abstract

:
In recent decades, environmental pollution has emerged as a core issue, around the globe, rendering it of fundamental concern to eco-toxicologists, environmental biologists, eco-chemists, pathologists, and researchers from other fields. The dissolution of polluting agents is a leading cause of environmental pollution of all key spheres including the hydrosphere, lithosphere, and biosphere, among others. The widespread occurrence of various pollutants including toxic heavy metals and other emerging hazardous contaminants is a serious concern. With increasing scientific knowledge, socioeconomic awareness, human health problems, and ecological apprehensions, people are more concerned about adverse health outcomes. Against this background, several removal methods have been proposed and implemented with the aim of addressing environmental pollution and sustainable and eco-friendly development. Among them, the biosorption of pollutants using naturally inspired sources, e.g., marine algae, has considerable advantages. In the past few years, marine algae have been extensively studied due to their natural origin, overall cost-effective ratio, and effectiveness against a broader pollutant range; thus, they are considered a potential alternative to the conventional methods used for environmental decontamination. Herein, an effort has been made to highlight the importance of marine algae as naturally inspired biosorbents and their role in biosorption. Biosorption mechanisms and factors affecting biosorption activities are also discussed in this review. The utilization of marine algae as a biosorbent for the removal of numerous potentially toxic elements has also been reviewed.

1. Introduction

Increasing pollution is one of the major problems that our ecosystem is facing both at the aquatic and the terrestrial level. Some of the sources of polluting agents include chemical byproducts, herbicides, pesticides, pharmaceuticals, cosmeceuticals, leather, textiles, the plastic industry, pigments, electroplating, storage batteries, mining, smelting, metallurgical processes, nanoparticles, etc. [1,2]. However, besides their technological importance, the abovementioned contaminants are included in the category of persistent and/or emerging environmental pollutants, because they cannot be destroyed or degraded [1,3,4]. Also, these polluting agents are a leading cause of environmental pollution in almost all the key spheres, including the hydrosphere, lithosphere, and biosphere [2,5]. In recent decades, environmental pollution has emerged as a core issue around the globe, rendering it of fundamental concern to eco-toxicologists, environmental biologists, eco-chemists, pathologists, and researchers from other fields. Owing to rapid industrial expansion and the continued growth of the human population, the consequences of environmental pollution are worse than ever. Therefore, advanced methods with unique redefining approaches are required to meet the demands of the growing world population. Such strategies of the so-called “green agenda” are nowadays equally important for the sustainable development of all modern societies.
So far, numerous detection and removal methods have been proposed and implemented with the aim of addressing environmental pollution and sustainable and eco-friendly development. Among them, fluorescent-based sensors and electrochemical sensors for detection purposes, immobilized enzyme-based catalytic systems and photocatalytic systems for degradation purposes, along with other physiochemical-based process, etc. are the most widely used, though each have certain advantages and disadvantages [1,4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20]. Therefore, advanced methods with unique redefining approaches are required to remove potentially toxic elements and other hazardous pollutants from aqueous environments. Considering the adverse health outcomes, a clean and sustainable environment is of great importance.
The recovery of potentially toxic elements such as silver, gold, and uranium from chemically treated aqueous solutions is cost-effective [21]. However, the treatment of potentially toxic elements in wastewater is a challenge not only from an economic point of view but also from an environmental one. In order to remove potentially toxic elements, various physiochemical techniques such as ion exchange [22], chemical precipitation [23], electrokinetics [24], adsorption [25], and membrane processing [26] have been employed. Physiochemical processes pose high costs due to the expensive chemicals required for treatment of potentially toxic elements. Incomplete removal of potentially toxic elements is another factor involved in physiochemical processes. Furthermore, stringent conditions placed by regulating authorities on effluents also demand alternative methods. Potentially toxic elements can be removed from wastewater through biosorption from algae, which is an efficient, safe, and more economical method. Algae are also used for sorption of heavy radionuclides [27] and can recover metal ions such as gold and silver [28]. However, removal of potentially toxic elements can be attained by acquiring knowledge of algae. Biosorption mechanisms for potentially toxic element removal include ion exchange and complex formation, whereas electrostatic interaction proceeds at the micro-level. For the biosorption of metals, ion exchange is an important mechanism [29,30].
In this context, naturally inspired sources/materials, e.g., the biosorbent potentialities of marine algae and algae-based compounds, have appeared as an alternative technology with special reference to biosorption (Figure 1). Natural sources are now considered ecologically safer, cheaper, and more efficient for removing toxic metal ions and other hazardous pollutants from aqueous environments, e.g., industrial wastewater [15]. As compared to other methods, biosorption is rapid, reversible, economical, and eco-friendly. Owing to its range of novel aspects, as mentioned above, biosorption can be used in several ways under numerous conditions to reduce environmental pollution. Naturally inspired biosorbents, e.g. marine algae, offer several advantages such as (1) diverse multifunctional groups on their surface, (2) relatively small and uniform distribution of binding sites on the surface, (3) requires minimal preparatory steps, (4) no or less consumption of harsh chemicals, (5) naturally renewable, recyclable, and easily available all year round, (6) excellent retention capacity, and so on. Based on the literature, the utilization of marine algae as biosorbents has been successfully tested for several biotechnological and industrial applications including the removal of various potentially toxic elements [15,31,32,33,34,35,36,37].

2. Marine Algae: Sources, Production Strategies, and Applied Perspectives

Marine life is full of biodiversity but little explained in terms of total species. Indeed, there exists a range of exceptional sources of microorganisms including plants and animals that show particular features. Algae are one such group and cover about 30,000 species from various phylogenetic groups. Broadly, algae can be categorized into two groups: (1) macroalgae (multicellular); and (2) microalgae (unicellular). However, algae are heterogeneous from an evolutionary point of view [39]. Coastal area algae are mostly macroalgae and classified into three types: Chlorophyred (green), Rhodophyceae (red), and Phaeophycea (brown) algae [34,35,37,40,41]. Microalgae are found as phytoplankton throughout the oceanic ecosystem [40]. Microalgae consist of varied species and present biochemical properties, particularly undertaking oxygen-mediated photosynthesis [42]. They can survive under less favorable conditions such as high salinity, heat, cold, varied light sources, osmotic pressure, and anaerobiosis. Microalgae are the main food producers for animals because of fatty acid, sterol, carbohydrate, mineral, vitamin, protein, tocopherols antioxidant, chlorophyll, and carotenoid production [43].
During photosynthesis, algae cells convert solar energy to chemical energy, which generates chemical compounds of biological activities known as bioactive compounds. Production of these bioactive compounds could be associated with microbial and algal growth [44]. The Dictionary of Marine Natural Products is a key data source, listing more than 30,000 bioactive compounds from algae, and that number is gradually increasing every year [45].
Production of photosynthetic microorganisms by autotrophic cultivation is increasing, mainly for to get useful biomolecules. Various methods have been developed for microalgae cultivation such as open pond cultivation and photobioreactor cultivation, including membrane, flat-plate, helicoidal, horizontal, and vertical photobioreactors [46]. For improved biomass composition, tubular reactors using airlift systems are most common. Heterotrophic conditions could also produce microalgae with sufficient nutrients, whereas in mesotrophic environments and the non-availability of light, nutrients are achieved heterotrophically as well as autotrophically [47].
Macroalgae, also known as seaweeds, are used for the production of phycocolloids such as agar and alginates [48]. Some macroalgae like brown and red algae are employed in cosmetics because of their sugar, mineral, lipid, vitamin, and amino acid contents, as well as some other biological compounds [48]. Algae have become a sustainable resource due to the growing demand for bioprocessing to obtain environmentally friendly products [49]. Recently, bioactive compounds from algae [37,48], have become important and are being utilized in various environment-related applications like biofuel production, CO2 sequestration, wastewater treatment, oxygen discharge to the environment, and reducing the effects of greenhouse gases [40,50].

3. Biosorption and Its Mechanisms

Different mechanisms have been reported for the removal of potentially toxic elements through biosorption. Previously, biosorption was categorized into metabolism-dependent or metabolism-independent biosorption [51]. However, later on, metabolism-dependent processes were termed bioaccumulation, and metabolic-independent processes were termed biosorption [52,53]. Bioaccumulation, also termed active biosorption, involves two processes: the first is similar to biosorption, involving attachment of potentially toxic elements to the surface; and in the second step active transportation of metal ions into cells occurs [54]. Biosorption is a passive process that occurs at a faster rate than bioaccumulation. Adsorption, chelation/complexation, ion exchange, and surface precipitation are different processes reportedly involved in biosorption (Figure 2) [55,56]. Among them, ion exchange is considered the principle mechanism of biosorption, which occurred through different functional groups present on the surface of biomass [53,57]. The mechanism of biosorption usually depends upon the biomass that is going to be used for the removal of potentially toxic elements [53]. For instance, the composition of the cell wall is different in bacteria (peptidoglycan), fungi (chitin), and algae (alginate, sulfonated polysaccharides); therefore, variation in the presence of functional groups on the surface of the cell wall is responsible for the difference in mechanisms [55,58]. Apart from the cell wall, extracellular polymer substances secreted by microorganisms are also found to play an important role in biosorption [59]. Verma et al. [60] reported ion exchange as a principle mechanism for the biosorption of potentially toxic elements by dry biomass of macrophytes. They presumed that aquatic macrophytes served as natural ion exchangers. Monovalent ions (H+, Na+/K+) were reported to be involved in the ion exchange process due to a weak attachment with biomass as compared to divalent ions [60]. Very recently, Ahmad et al. [61] reported that sulfate, carboxyl, and hydroxyl groups are involved in biosorption by microalgae. Changing of the morphological structure observed by scanning electron microscope (SEM) and/or energy dispersive X-ray (EDX) after biosorption also indicated the facilitation of sorption of metal ions by pores present on the surface [61]. However, in general, the mechanism of metal ion absorption by biomass is complicated and involves different processes.

4. Factors Affecting Biosorption

Different factors can influence biosorption processes such as pH, temperature, initial metallic concentration, contact time, competing ions/co-ions, and biosorbent dosage [38,61,62]. Among these factors, pH is the most important factor. Increase in pH also increases the biosorption of metal ions, however; too great an increase in pH can cause precipitation, which should be avoided [62]. Optimum pH varied for different biosorption systems. An increase in pH up to 5 caused an increase in biosorption capacity (98%), but a further increase in pH led to reduced capacity. Protonation and deprotonation of functional groups is controlled by the pH of the medium, which affects the biosorption capacity: at low pH, carboxylic groups, being acidic, exist in a protonated state due to the presence of excess H+ and H3O+; therefore, repulsive forces of these protonated groups with positively charged heavy metal ions are responsible for the lower biosorption capacity at low pH [61,63]. With the increase in pH, functional groups such as amine, carboxyl, and hydroxyl groups are exposed by deprotonation, which enhances electrostatic attraction with heavy metal ions due to a negative charge. The high increase in pH leads to the formation of hydroxide anionic complexes and precipitation is a reported reason for the low biosorption capacity [61,63,64,65].
Temperature is also an important parameter influencing the sorption process [55]. Change in temperature alters thermodynamic parameters, resulting in variation in sorption capacity [38]. The influence of temperature on the sorption process depends upon its nature. In endothermic sorption processes, an increase in temperature leads to an increase in biosorption; on the other hand, an increase in temperature decreases biosorption in the case of exothermic sorption processes [38]. For instance, the biosorption of Pb(II) by algae was found to increase with an increase in temperature [66]. The biosorption of Pb(II), Cd(II), and Co(II), from an aqueous solution on green algae waste biomass has also been reported [16]. In another report, Ahmad et al. [61] found a reduction in biosorption of Fe(II), Mn(II), and Zn(II) by freely suspended and Ca–alginate immobilized with Chlorella vulgaris with an increase in temperature (25–45 °C) due to the exothermic nature of the biosorption process. A very high temperature can also denature the biomass structure [61].
The contact time of biosorbent influences total biosorption. An increase in contact time up to the optimum contact time increases biosorption; afterwards it becomes relatively constant. Occupancy of all active sites causes saturation of biomass, leading to an equilibrium state [63,67]. The optimum time is different for different types of biosorbents such as 60 min for red macroalgae [63] and 300 min for immobilized algal mass (240 min for free suspended mass) [61]. The initial metal ionic strength also affects biosorption. A high initial metallic concentration exhibits high biosorption capacity due to the availability of free active sites [68]. A similar trend was also reported by changing the adsorbent dose, i.e., initial increase and then equilibrium state [69,70].

5. Potential Biosorbents

For biosorption purposes, different living and non-living biomasses have been reported such as algal biomass, fungi, bacteria, agricultural waste, etc. [71]. Typically, an ideal biosorbent should possess features like availability, non-toxicity, high metal binding capacity, large-scale usability, and regeneration/re-usability [21]. Algal biomass is the most employed biosorbent compared to any other material. As no treatment is required for algae, it is considered a low-cost biosorbent, and its cell wall characteristics endow it with high metal ion binding capacity [72]. Non-living algal mass has been reported to be more promising as compared to living algae because of the higher metal ions sorption capacity at a higher rate, and it does not require nutrients grown in a medium [38]. Moreover, adsorbed heavy metal ions on dead algal mass can be removed using de-ionized water or desorption agents [38]. Different types of algae have been reported as biosorbents such as marine algae, marine red macroalgae, marine brown macroalgae, and freshwater green macroalgae. Brown algae are reported to have good biosorption capacity due to the presence of alginates in their cell walls [73].

6. Potentially Toxic Elements—Heavy Metals

Heavy metals exist naturally in the earth’s crust and are distributed in the soil. While there is no clear definition for heavy metals, density is the defining element in most situations. Conventionally, on the periodic table, heavy metals are those with an atomic number greater than 20 [65]. Considering their atomic density higher than 4 g cm−3 (5 times higher than water), they form a group of about 53, including metals and elements with metallic properties [74]. Heavy metals are referred to as high-density elements and cause toxicity at low strengths. Nevertheless, from an ecological point of view, any metal or related metalloid that is not biodegradable and produces environmental pollution can be taken as a heavy metal [74]. Some heavy metals (e.g., Cu, Zn, Ni, Cu, Mn, and Co) are essential for plant life, whereas some do not have any biological role and have toxic effects (e.g., Pb, Hg, and Cd) [75]. Therefore, any metal or metalloid that causes a harmful effect on the environment, does not play a vital role in biological functions, shows toxicity at low strengths (e.g., Pb and Hg), or plays a vital role in biological functions but produces harmful effects if present in a high concentration (e.g., Cu and Mo) [74]. Wang and Chen [21] classified harmful heavy metals into three divisions: toxic metals (Pb, Hg, Zn, Cr, Ni, Co Cd, Cu, Sn, As, etc.), radionuclides (U, Th, Am, Ra, etc.), and precious metals (Au, Ag, Pt, Ru, etc.).
Urbanization, industrialization, population growth, and continuous cultivation have damaged the global environment. The toxic effects and major mechanisms of toxicity of different heavy metals are summarized in Table 1. Human activities and industrial applications of heavy metals have increased toxicity levels and pose harmful effects to the environment [74,76]. Several reports report the varied use of heavy metals [77] in different industrial [21] and agrarian practices [78], in addition to indiscriminate disposal [79]. Among the other harmful effects of heavy metals, water pollution is one of the serious issues worldwide [80]. Several heavy metals released into the environment by different activities undergo transformations, are dispersed and accumulated in the food chain, and cause serious health concerns [81]. In short, removal of heavy metals is a challenge as they are not biodegradable and hence hinder the self-purification capability of marine life when discharged to the aquatic environment [82].

7. Biosorption of Potentially Toxic Elements

Potentially toxic elements are removed from wastewater by algae, mostly through inactive biomass and non-living algae. Fewer data are available on using live algae for potentially toxic element removal [103], as toxic elements poison the algae. Although sorption largely depends on the stage of the algae growth, there are several factors that affect the biosorption of metal ions. The process of biosorption is more complicated in living algae as compared to non-living algae as biosorption occurs in the growth stage and the intracellular consumption of potentially toxic elements mostly takes place at this stage. The cells of non-living algae absorb potentially toxic elements at the cell membrane surface. Therefore, the process is known as an extracellular process [104]. Non-living algal biomass includes polymers such as sugars, glycoproteins, cellulose, pectins, etc., which effectively bind and adsorb potentially toxic elements from wastewater [105]. Two stages are involved in the accumulation of potentially toxic elements through microorganisms [106]. During the first stage, fast inactive biosorption proceeds at the cell surface with no cellular metabolism involved, whereas active sorption occurs during the second stage, which involves the cell cytoplasm. The second stage is considered intracellular ion accumulation since it involves cell metabolism. Intercellular ion accumulation plays a vital role in the biosorption detoxification of potentially toxic elements [107].
The biosorption ability of algae cell surface is designated by the availability of the binding moiety, i.e., carboxyl, hydroxyl, amine, phosphoryl, sulphuryl, sulfate, carbohydrate, imidazole, phosphate, etc. [108]. The presence of the binding site on the algae cell for potentially toxic elements accumulation is analyzed by Fourier-transform infrared spectroscopy (FTIR) spectroscopy [109]. Accumulation of the potentially toxic elements on the algae cell depends on various factors such as the number of functional moieties, the approachability of binding sites, binding constants, and the chemical state of the moieties. Most binding moieties make the cell surface negatively charged overall as a result of carboxyl and phosphate deprotonation [110]. Biosorption of the metal ions starts from the algae cell wall. Various binding groups, for example OH−, COO−, NO3−, RS−, SH−, PO43−, RNH2− and RO− encourage adsorption of the metal ions. These groups exist outside (cell surface) and inside (cytoplasm and vacuoles) the cell wall. The biosorption mechanism of metal ions across the cell walls could be supported by cytosolic protein-mediated metal ions transfer [111]. Vacuoles, therefore, accumulate metal ions and are considered metal ion organelles. The data based on the affinity for various metal ions and the corresponding cellular ligands are illustrated in Figure 3. Ligands with R present alkyl groups, for example propyl and metal ions categorized into A, B, and borderline subcategories. Category I shows the connection of ligands with metal ions of Class A through an oxygen atom. Metal ions from Class B can be connected with ligands of category II and III, whereas borderline cations can be associated with various atoms from categories I, II, and III [52]. The categorization is well defined, but it would be more convenient if the classification is based on metal complexation constants from a chemistry viewpoint. This can be more helpful for scientists trying to decide on the biosorption ability of a particular metal among competing ions.
The cell wall in algae cells is an initial hindrance to the biosorption of potentially toxic elements. Most of the binding sites present in algae cells are due to polysaccharides and proteins [112]. Different algal strains have different cell wall compositions and varying capacity of biosorption of potentially toxic elements. Romera et al. [113] studied different algae strains for the biosorption of potentially toxic elements and proposed brown algae as a good contender. Brown algae have a high affinity for the biosorption of lead because of the presence of alginate in the cell walls and the capacity of biosorption depends on the binding sites available on the alginate [32,113]. Several factors such as metal ion concentration, competing for metal ions, temperature, and pH affect the biosorption of potentially toxic elements in addition to available binding sites on the algae cell.

7.1. Biosorption of Cadmium

Cadmium is found in nature in the form of deposits with other elements. The toxic metal is discharged in industrial effluents from phosphate fertilizers, plating, stabilizers, and cadmium–nickel alloy batteries. Low concentrations of cadmium can accumulate and become harmful to the ecosystem. Cadmium can cause “Itai-itai” bone softening and fractures in humans [114]. Other effects of cadmium on human health include lung cancer, kidney failure, and damage to respiratory and reproductive systems [115,116]. Therefore, efficient, reliable, and economical removal of cadmium from water is required. Biosorption of cadmium using marine algae is a safe, useful, and eco-friendly solution to wastewater treatment. Table 2 presents various algae’s capacity to remove potentially toxic elements. The table comprises Cd2+ removal in the pH range from 4 to 8. It has been found that algae C. reinhardtii, Scevedesmus spp., S. platensis, Chlorella spp. as well as Tetraselmis spp. efficiently remove Cd2+, whereas the uptake of Cd2+ from Plaothidium lanceolatum live cells is significant, i.e. 275.51 mg g−1 [117].

7.2. Biosorption of Chromium

Chromium is the seventh most prevalent metal on earth and is found in ores with other metals like chromite (FeCr2O3), chrome ochre (Cr2O3), and crocoite (PbCrO3). The foremost industrial sources of chromium are the leather, tanning, textile, and electroplating industries. Industry waste has hexavalent and trivalent ions of chromium, i.e., Cr6+ and Cr3+ [129]. Cr3+ is less toxic to living organisms than Cr6+ [116,130]. Cr3+ is helpful in sugar and fat metabolism, and Cr6+ is used in industry for salt production [129,131]. Both states of chromium metals are used for chrome plating, pigment fabrication, in the glass industry, in the leather industry as a tanning agent, etc. [132]. They damage organs such as the liver, kidneys, and skin and can cause ulcers, pulmonary congestion, and vomiting [132,133]. In order to reduce the effects of chromium, it needs to be modified to a less toxic state and treated before release into the environment.

7.3. Biosorption of Lead

Lead is also a toxic metal that can easily accumulate in plants, the human body, and other living organisms. It is found in nature in the state of sulfide, cerussite (PbCl2) ore, and galena [134]. Wastewater from industries such as electrical, steel, electroplating, explosives, etc. is the main source of lead pollution. Its function is to produce DNA, protein, and replication of the cell [134]. It is harmful to the nervous system, kidneys, and mental health and causes cancer in humans [135,136]. Lead is also toxic to plants and animals. Therefore, the latest techniques are required to remove lead from water. Biosorption through algae is an innovative technique for the removal of lead from the ecosystem. As mentioned in Table 2, Spirulina as well as Chlorella ssp. algae show potential for Pb2+ removal capacity. Also, significant results have been achieved for lead removal with immobilized cells, i.e., C. reinhardtii [125].

7.4. Biosorption of Zinc

Zinc is helpful in various biochemical processes and controls physiological mechanisms in living tissues. With other metals (such as steel alloys), it works as a protective layer to control corrosion. Other forms of zinc are used in industrial processes like steel, mining, and coal combustion [137]. Although a trace amount of zinc is required by the body, if present in excess amounts it can upset normal health. It can cause fever, pain, skin inflammation, vomiting, and anemia [137]. Sources of zinc pollution in the ecosystem are the paper, steel, electroplating, and brass industries. Given the effects of zinc metals, it becomes important to treat wastewater effectively before releasing it into the environment. Zinc has been studied for biosorption in the pH range from 5 to 7.5 (Table 2). P. lanceolatum algae are a potential contender to remove zinc metal up to 118.66 mg g−1 [117].

8. Concluding Remarks and Future Considerations

In conclusion, the above data suggest that the effective removal of potentially toxic elements from aqueous media can be achieved by biosorption using marine algae biomass as a biosorbent. Naturally inspired biosorbents, e.g., marine algae, offer several advantages such as (1) diverse multifunctional groups on their surface, (2) relatively small and uniform distribution of binding sites on the surface, (3) requiring minimal preparatory steps, (4) no or less consumption of harsh chemicals, (5) being naturally renewable, recyclable, and easily available all year round, (6) excellent retention capacity, and so on.
Despite the modern expansion of the biotechnological and industrial arena, along with the plethora of information available on various types of bioremediation processes, numerous challenges still need to be addressed. For example, the emergence of new pollutants, potentially toxic elements’ dissemination profiles, eco-friendly detection, removal fate, and reliable and consistent monitoring are research gaps that need to be addressed in future studies. In this context, proper management and strategies should be adapted to maintain aquatic and terrestrial environmental health and protect from further deterioration.
Furthermore, many other unsolved questions must be tackled. For example, insufficient detection methods, malpractice, and limitations within practice technologies greatly affect the detection fate and removal behavior of potentially toxic elements. The role of low-risk contaminants in the emergence of new pollutants should also be addressed in future studies. It could be useful to involve multidisciplinary scientists, policymakers, and stakeholders to strengthen the detection and removal/degradation of life-threatening pollutants at a global level.

Acknowledgments

The literature facilities provided by Shanghai Jiao Tong University, Shanghai 200240, China and Tecnologico de Monterrey, Mexico are thankfully acknowledged.

Author Contributions

Muhammad Bilal and Hafiz M. N. Iqbal designed the review contents; Tahir Rasheed, Ali Raza, and Faran Nabeel reviewed the literature; Juan Eduardo Sosa-Hernández and Ali Raza designed the figures and tables; Muhammad Bilal and Hafiz M. N. Iqbal critically reviewed and revised the paper. All authors read and approved the final manuscript.

Conflicts of Interest

The authors report no conflicting interest in any capacity, competing or financial.

References

  1. Ahmed, I.; Iqbal, H.M.N.; Dhama, K. Enzyme-based biodegradation of hazardous pollutants—An overview. J. Exp. Biol. Agric. Sci. 2017, 5, 402–411. [Google Scholar] [CrossRef]
  2. Ullah, S.; Zuberi, A.; Alagawany, M.; Farag, M.R.; Dadar, M.; Karthik, K.; Tiwari, R.; Dhama, K.; Iqbal, H.M.N. Cypermethrin induced toxicities in fish and adverse health outcomes: Its prevention and control measure adaptation. J. Environ. Manag. 2018, 206, 863–871. [Google Scholar] [CrossRef] [PubMed]
  3. Park, D.; Yun, Y.S.; Park, J.M. The past, present, and future trends of biosorption. Biotechnol. Bioproc. Eng. 2010, 15, 86–102. [Google Scholar] [CrossRef]
  4. Barrios-Estrada, C.; de Jesús Rostro-Alanis, M.; Muñoz-Gutiérrez, B.D.; Iqbal, H.M.N.; Kannan, S.; Parra-Saldívar, R. Emergent contaminants: Endocrine disruptors and their laccase-assisted degradation―A review. Sci. Total Environ. 2018, 612, 1516–1531. [Google Scholar] [CrossRef] [PubMed]
  5. Rasheed, T.; Bilal, M.; Nabeel, F.; Iqbal, H.M.N.; Li, C.; Zhou, Y. Fluorescent sensor based models for the detection of environmentally-related toxic heavy metals. Sci. Total Environ. 2018, 615, 476–485. [Google Scholar] [CrossRef] [PubMed]
  6. Bilal, M.; Iqbal, H.M.N.; Shah, S.Z.H.; Hu, H.; Wang, W.; Zhang, X. Horseradish peroxidase-assisted approach to decolorize and detoxify dye pollutants in a packed bed bioreactor. J. Environ. Manag. 2016, 183, 836–842. [Google Scholar] [CrossRef] [PubMed]
  7. Barrios-Estrada, C.; de Jesús Rostro-Alanis, M.; Parra, A.L.; Belleville, M.P.; Sanchez-Marcano, J.; Iqbal, H.M.N.; Parra-Saldívar, R. Potentialities of active membranes with immobilized laccase for Bisphenol A degradation. Int. J. Biol. Macromol. 2017, 108, 837–844. [Google Scholar] [CrossRef] [PubMed]
  8. Bilal, M.; Rasheed, T.; Iqbal, H.M.N.; Hu, H.; Wang, W.; Zhang, X. Novel characteristics of horseradish peroxidase immobilized onto the polyvinyl alcohol-alginate beads and its methyl orange degradation potential. Int. J. Biol. Macromol. 2017, 105, 328–335. [Google Scholar] [CrossRef] [PubMed]
  9. Bilal, M.; Asgher, M.; Iqbal, H.M.N.; Hu, H.; Wang, W.; Zhang, X. Bio-catalytic performance and dye-based industrial pollutants degradation potential of agarose-immobilized MnP using a Packed Bed Reactor System. Int. J. Biol. Macromol. 2017, 102, 582–590. [Google Scholar] [CrossRef] [PubMed]
  10. Bilal, M.; Asgher, M.; Iqbal, H.M.N.; Hu, H.; Zhang, X. Bio-based degradation of emerging endocrine-disrupting and dye-based pollutants using cross-linked enzyme aggregates. Environ. Sci. Pollut. Res. 2017, 24, 7035–7041. [Google Scholar] [CrossRef] [PubMed]
  11. Bilal, M.; Iqbal, H.M.N.; Hu, H.; Wang, W.; Zhang, X. Development of horseradish peroxidase-based cross-linked enzyme aggregates and their environmental exploitation for bioremediation purposes. J. Environ. Manag. 2017, 188, 137–143. [Google Scholar] [CrossRef] [PubMed]
  12. Bilal, M.; Asgher, M.; Parra-Saldivar, R.; Hu, H.; Wang, W.; Zhang, X.; Iqbal, H.M.N. Immobilized ligninolytic enzymes: An innovative and environmental responsive technology to tackle dye-based industrial pollutants―A review. Sci. Total Environ. 2017, 576, 646–659. [Google Scholar] [CrossRef] [PubMed]
  13. Belkhamssa, N.; Rocha-Santos, T.; Ksibi, M. Development of Electrochemical Immunosensors for Endocrine Disrupting Detection. In Euro-Mediterranean Conference for Environmental Integration; Springer: Cham, Switzerland, 2017; pp. 305–306. [Google Scholar]
  14. Chatha, S.A.S.; Asgher, M.; Iqbal, H.M.N. Enzyme-based solutions for textile processing and dye contaminant biodegradation―A review. Environ. Sci. Pollut. Res. 2017, 24, 14005–14018. [Google Scholar] [CrossRef] [PubMed]
  15. Bulgariu, L.; Bulgariu, D. Sustainable Utilization of Marine Algae Biomass for Environmental Bioremediation. In Prospects and Challenges in Algal Biotechnology; Springer: Singapore, 2017; pp. 179–217. [Google Scholar]
  16. Bulgariu, D.; Bulgariu, L. Equilibrium and kinetics studies of heavy metal ions biosorption on green algae waste biomass. Bioresour. Technol. 2012, 103, 489–493. [Google Scholar] [CrossRef] [PubMed]
  17. Justino, C.I.; Duarte, A.C.; Rocha-Santos, T.A. Recent Progress in Biosensors for Environmental Monitoring: A Review. Sensors 2017, 17, 2918. [Google Scholar] [CrossRef] [PubMed]
  18. Nogueira, V.; Lopes, I.; Rocha-Santos, T.A.P.; Gonçalves, F.; Pereira, R. Treatment of real industrial wastewaters through nano-TiO2 and nano-Fe2O3 photocatalysis: Case study of mining and kraft pulp mill effluents. Environ. Technol. 2017. [Google Scholar] [CrossRef] [PubMed]
  19. Rasheed, T.; Bilal, M.; Iqbal, H.M.N.; Hu, H.; Zhang, X. Reaction mechanism and degradation pathway of rhodamine 6G by photocatalytic treatment. Water Air Soil Pollut. 2017, 228. [Google Scholar] [CrossRef]
  20. Bilal, M.; Rasheed, T.; Iqbal, H.M.N.; Hu, H.; Wang, W.; Zhang, X. Toxicological Assessment and UV/TiO2-Based Induced Degradation Profile of Reactive Black 5 Dye. Environ. Manag. 2018, 61, 171–180. [Google Scholar] [CrossRef] [PubMed]
  21. Wang, J.; Chen, C. Biosorbents for heavy metals removal and their future. Biotechnol. Adv. 2009, 27, 195–226. [Google Scholar] [CrossRef] [PubMed]
  22. Da̧browski, A.; Hubicki, Z.; Podkościelny, P.; Robens, E. Selective removal of the heavy metal ions from waters and industrial wastewaters by ion-exchange method. Chemosphere 2004, 56, 91–106. [Google Scholar] [CrossRef] [PubMed]
  23. Charerntanyarak, L. Heavy metals removal by chemical coagulation and precipitation. Water Sci. Technol. 1999, 39, 135–138. [Google Scholar]
  24. Yuan, C.; Weng, C.H. Electrokinetic enhancement removal of heavy metals from industrial wastewater sludge. Chemosphere 2006, 65, 88–96. [Google Scholar] [CrossRef] [PubMed]
  25. Lee, S.M.; Laldawngliana, C.; Tiwari, D. Iron oxide nano-particles-immobilized-sand material in the treatment of Cu (II), Cd (II) and Pb (II) contaminated waste waters. Chem. Eng. J. 2012, 195, 103–111. [Google Scholar] [CrossRef]
  26. Qdais, H.A.; Moussa, H. Removal of heavy metals from wastewater by membrane processes: A comparative study. Desalination 2004, 164, 105–110. [Google Scholar] [CrossRef]
  27. Pohl, P.; Schimmack, W. Adsorption of radionuclides (134Cs, 85Sr, 226Ra, 241Am) by extracted biomasses of cyanobacteria (Nostoc Carneum, N. Insulare, Oscillatoria Geminata and Spirulina Laxis-Sima) and phaeophyceae (Laminaria Digitata and L. Japonica; waste products from alginate production) at different pH. J. Appl. Phycol. 2006, 18, 135–143. [Google Scholar]
  28. Mata, Y.N.; Torres, E.; Blazquez, M.L.; Ballester, A.; González, F.M.J.A.; Munoz, J.A. Gold (III) biosorption and bioreduction with the brown alga Fucus vesiculosus. J. Hazard. Mater. 2009, 166, 612–618. [Google Scholar] [CrossRef] [PubMed]
  29. Mehta, S.K.; Singh, A.; Gaur, J.P. Kinetics of adsorption and uptake of Cu2+ by Chlorella vulgaris: Influence of pH, temperature, culture age, and cations. J. Environ. Sci. Heal. A 2002, 37, 399–414. [Google Scholar] [CrossRef]
  30. Michalak, I.; Chojnacka, K. Interactions of metal cations with anionic groups on the cell wall of the macroalga Vaucheria sp. Eng. Life Sci. 2010, 10, 209–217. [Google Scholar] [CrossRef]
  31. Dönmez, G.Ç.; Aksu, Z.; Öztürk, A.; Kutsal, T. A comparative study on heavy metal biosorption characteristics of some algae. Process Biochem. 1999, 34, 885–892. [Google Scholar] [CrossRef]
  32. Davis, T.A.; Volesky, B.; Mucci, A. A review of the biochemistry of heavy metal biosorption by brown algae. Water Res. 2003, 37, 4311–4330. [Google Scholar] [CrossRef]
  33. Romera, E.; González, F.; Ballester, A.; Blázquez, M.L.; Munoz, J.A. Comparative study of biosorption of heavy metals using different types of algae. Bioresour. Technol. 2007, 98, 3344–3353. [Google Scholar] [CrossRef] [PubMed]
  34. Bilal, M.; Rasheed, T.; Ahmed, I.; Iqbal, H.M.N. High-value compounds from microalgae with industrial exploitability―A review. Front. Biosci. (Sch. Ed.) 2017, 9, 319–342. [Google Scholar] [PubMed]
  35. Centella, M.H.; Arévalo-Gallegos, A.; Parra-Saldivar, R.; Iqbal, H.M.N. Marine-derived bioactive compounds for value-added applications in bio-and non-bio sectors. J. Clean. Prod. 2017, 168, 1559–1565. [Google Scholar] [CrossRef]
  36. Parsaeimehr, A.; Mancera-Andrade, E.I.; Robledo-Padilla, F.; Iqbal, H.M.N.; Parra-Saldivar, R. A chemical approach to manipulate the algal growth, lipid content and high-value alpha-linolenic acid for biodiesel production. Algal Res. 2017, 26, 312–322. [Google Scholar] [CrossRef]
  37. Bule, M.H.; Ahmed, I.; Maqbool, F.; Bilal, M.; Iqbal, H.M.N. Microalgae as a source of high-value bioactive compounds. Front. Biosci. (Sch. Ed.) 2018, 10, 197–216. [Google Scholar] [PubMed]
  38. Zeraatkar, A.K.; Ahmadzadeh, H.; Talebi, A.F.; Moheimani, N.R.; McHenry, M.P. Potential use of algae for heavy metal bioremediation, a critical review. J. Environ. Manag. 2016, 181, 817–831. [Google Scholar] [CrossRef] [PubMed]
  39. Sasso, S.; Pohnert, G.; Lohr, M.; Mittag, M.; Hertweck, C. Microalgae in the postgenomic era: A blooming reservoir for new natural products. FEMS Microbial. Rev. 2012, 36, 761–785. [Google Scholar] [CrossRef] [PubMed]
  40. Wang, H.M.D.; Chen, C.C.; Huynh, P.; Chang, J.S. Exploring the potential of using algae in cosmetics. Bioresour. Technol. 2015, 184, 355–362. [Google Scholar] [CrossRef] [PubMed]
  41. Chandra, R.; Parra, R.; Iqbal, H.M.N. Phycobiliproteins: A Novel Green Tool from Marine Origin Blue-Green Algae and Red Algae. Protein Peptide Lett. 2017, 24, 118–125. [Google Scholar] [CrossRef] [PubMed]
  42. Dionisio-Sese, M.L. Aquatic microalgae as potential sources of UV-screening compounds. Philippine J. Sci. 2010, 139, 5–16. [Google Scholar]
  43. Borowitzka, M.A. High-value products from microalgae—Their development and commercialisation. J. Appl. Phycol. 2013, 25, 743–756. [Google Scholar] [CrossRef]
  44. Burja, A.M.; Banaigs, B.; Abou-Mansour, E.; Burgess, J.G.; Wright, P.C. Marine cyanobacteria—A prolific source of natural products. Tetrahedron 2001, 57, 9347–9377. [Google Scholar] [CrossRef]
  45. Kiuru, P.; D’Auria, M.V.; Muller, C.D.; Tammela, P.; Vuorela, H.; Yli-Kauhaluoma, J. Exploring marine resources for bioactive compounds. Planta Med. 2014, 80, 1234–1246. [Google Scholar] [CrossRef] [PubMed]
  46. Huang, J.; Li, Y.; Wan, M.; Yan, Y.; Feng, F.; Qu, X.; Wang, J.; Shen, G.; Li, W.; Fan, J.; Wang, W. Novel flat-plate photobioreactors for microalgae cultivation with special mixers to promote mixing along the light gradient. Bioresour. Technol. 2014, 159, 8–16. [Google Scholar] [CrossRef] [PubMed]
  47. Ariede, M.B.; Candido, T.M.; Jacome, A.L.M.; Velasco, M.V.R.; de Carvalho, J.C.M.; Baby, A.R. Cosmetic attributes of algae-A review. Algal Res. 2017, 25, 483–487. [Google Scholar] [CrossRef]
  48. Sanghvi, A.; Martin Lo, Y. Present and potential industrial applications of macro-and microalgae. Recent Pat. Food Nutr. Agric. 2010, 2, 187–194. [Google Scholar] [CrossRef] [PubMed]
  49. Yun, E.J.; Choi, I.G.; Kim, K.H. Red macroalgae as a sustainable resource for bio-based products. Trends Biotechnol. 2015, 33, 247–249. [Google Scholar] [CrossRef] [PubMed]
  50. Suganya, T.; Varman, M.; Masjuki, H.H.; Renganathan, S. Macroalgae and microalgae as a potential source for commercial applications along with biofuels production: A biorefinery approach. Renew. Sustain. Energy Rev. 2016, 55, 909–941. [Google Scholar] [CrossRef]
  51. Veglio, F.; Beolchini, F. Removal of metals by biosorption: A review. Hydrometallurgay 1997, 44, 301–316. [Google Scholar] [CrossRef]
  52. Volesky, B. Biosorption and me. Water Res. 2007, 41, 4017–4029. [Google Scholar] [CrossRef] [PubMed]
  53. Chojnacka, K. Biosorption and bioaccumulation―The prospects for practical applications. Environ. Int. 2010, 36, 299–307. [Google Scholar] [CrossRef] [PubMed]
  54. Flouty, R.; Estephane, G. Bioaccumulation and biosorption of copper and lead by a unicellular algae Chlamydomonas reinhardtii in single and binary metal systems: A comparative study. J. Environ. Manag. 2012, 111, 106–114. [Google Scholar] [CrossRef] [PubMed]
  55. Farooq, U.; Kozinski, J.A.; Khan, M.A.; Athar, M. Biosorption of heavy metal ions using wheat based biosorbents―A review of the recent literature. Bioresour. Technol. 2010, 101, 5043–5053. [Google Scholar] [CrossRef] [PubMed]
  56. El Hameed, A.H.A.; Eweda, W.E.; Abou-Taleb, K.A.; Mira, H.I. Biosorption of uranium and heavy metals using some local fungi isolated from phosphatic fertilizers. Ann. Agric. Sci. 2015, 60, 345–351. [Google Scholar] [CrossRef]
  57. Vijayaraghavan, K.; Balasubramanian, R. Is biosorption suitable for decontamination of metal-bearing wastewaters? A critical review on the state-of-the-art of biosorption processes and future directions. J. Environ. Manag. 2015, 160, 283–296. [Google Scholar] [CrossRef] [PubMed]
  58. Vijayaraghavan, K.; Yun, Y.S. Bacterial biosorbents and biosorption. Biotechnol. Adv. 2008, 26, 266–291. [Google Scholar] [CrossRef] [PubMed]
  59. Li, W.W.; Yu, H.Q. Insight into the roles of microbial extracellular polymer substances in metal biosorption. Bioresour. Technol. 2014, 160, 15–23. [Google Scholar] [CrossRef] [PubMed]
  60. Verma, V.K.; Tewari, S.; Rai, J.P.N. Ion exchange during heavy metal bio-sorption from aqueous solution by dried biomass of macrophytes. Bioresour. Technol. 2008, 99, 1932–1938. [Google Scholar] [CrossRef] [PubMed]
  61. Ahmad, A.; Bhat, A.H.; Buang, A. Biosorption of transition metals by freely suspended and Ca-alginate immobilised with Chlorella vulgaris: Kinetic and equilibrium modeling. J. Clean. Prod. 2018, 171, 1361–1375. [Google Scholar] [CrossRef]
  62. Wang, J.; Chen, C. Biosorption of heavy metals by Saccharomyces cerevisiae: A review. Biotechnol. Adv. 2006, 24, 427–451. [Google Scholar] [CrossRef] [PubMed]
  63. Ibrahim, W.M. Biosorption of heavy metal ions from aqueous solution by red macroalgae. J. Hazard. Mater. 2011, 192, 1827–1835. [Google Scholar] [CrossRef] [PubMed]
  64. Kumar, Y.P.; King, P.; Prasad, V.S.R.K. Removal of copper from aqueous solution using Ulva fasciata sp.—A marine green algae. J. Hazard. Mater. 2006, 137, 367–373. [Google Scholar] [CrossRef] [PubMed]
  65. Jiang, L.; Zhou, W.; Liu, D.; Liu, T.; Wang, Z. Biosorption isotherm study of Cd2+, Pb2+ and Zn2+ biosorption onto marine bacterium Pseudoalteromonas sp. SCSE709-6 in multiple systems. J. Mol. Liq. 2017, 247, 230–237. [Google Scholar] [CrossRef]
  66. Brouers, F.; Al-Musawi, T.J. On the optimal use of isotherm models for the characterization of biosorption of lead onto algae. J. Mol. Liq. 2015, 212, 46–51. [Google Scholar] [CrossRef]
  67. Ibrahim, W.M.; Hassan, A.F.; Azab, Y.A. Biosorption of toxic heavy metals from aqueous solution by Ulva lactuca activated carbon. Egypt. J. Basic Appl. Sci. 2016, 3, 241–249. [Google Scholar] [CrossRef]
  68. Vendruscolo, F.; da Rocha Ferreira, G.L.; Antoniosi Filho, N.R. Biosorption of hexavalent chromium by microorganisms. Int. Biodeter. Biodegr. 2017, 119, 87–95. [Google Scholar] [CrossRef]
  69. Sivaprakash, K.; Adlin Blessi, T.L.; Madhavan, J. Biosorption of Nickel from Industrial Wastewater using Zygnema sp. J. Inst. Eng. (India) Ser. A 2015, 96, 319–326. [Google Scholar] [CrossRef]
  70. Torab-Mostaedi, M.; Asadollahzadeh, M.; Hemmati, A.; Khosravi, A. Biosorption of lanthanum and cerium from aqueous solutions by grapefruit peel: Equilibrium, kinetic and thermodynamic studies. Res. Chem. Int. 2015, 41, 559–573. [Google Scholar] [CrossRef]
  71. Carolin, C.F.; Kumar, P.S.; Saravanan, A.; Joshiba, G.J.; Naushad, M. Efficient Techniques for the Removal of Toxic Heavy Metals from Aquatic Environment: A Review. J. Environ. Chem. Eng. 2017, 5, 2782–2799. [Google Scholar] [CrossRef]
  72. Anastopoulos, I.; Kyzas, G.Z. Progress in batch biosorption of heavy metals onto algae. J. Mol. Liq. 2015, 209, 77–86. [Google Scholar] [CrossRef]
  73. Demey, H.; Vincent, T.; Guibal, E. A novel algal-based sorbent for heavy metal removal. Chem. Eng. J. 2018, 332, 582–595. [Google Scholar] [CrossRef]
  74. Herrera-Estrella, L.R.; Guevara-Garcia, A.A. Heavy metal adaptation. In Encyclopedia of Life Sciences (ELS); John Wiley & Sons, Ltd.: Chichester, UK, 2009; pp. 1–9. [Google Scholar]
  75. Gaur, A.; Adholeya, A. Prospects of arbuscular mycorrhizal fungi in phytoremediation of heavy metal contaminated soils. Curr. Sci. 2004, 86, 528–534. [Google Scholar]
  76. Lasat, M.M. Phytoextraction of metals from contaminated soil: A review of plant/soil/metal interaction and assessment of pertinent agronomic issues. J. Hazard. Subst. Res. 1999, 2. [Google Scholar] [CrossRef]
  77. Torres, M.A.; Barros, M.P.; Campos, S.C.; Pinto, E.; Rajamani, S.; Sayre, R.T.; Colepicolo, P. Biochemical biomarkers in algae and marine pollution: A review. Ecotoxicol. Environ. Saf. 2008, 71, 1–15. [Google Scholar] [CrossRef] [PubMed]
  78. Brower, J.B.; Ryan, R.L.; Pazirandeh, M. Comparison of ion-exchange resins and biosorbents for the removal of heavy metals from plating factory wastewater. Environ. Sci. Technol. 1997, 31, 2910–2914. [Google Scholar] [CrossRef]
  79. Duffus, J.H. “Heavy metals” a meaningless term? (IUPAC Technical Report). Pure Appl. Chem. 2002, 74, 793–807. [Google Scholar] [CrossRef]
  80. Hong, K.S.; Lee, H.M.; Bae, J.S.; Ha, M.G.; Jin, J.S.; Hong, T.E.; Kim, J.P.; Jeong, E.D. Removal of heavy metal ions by using calcium carbonate extracted from starfish treated by protease and amylase. J. Anal. Sci. Technol. 2011, 2, 75–82. [Google Scholar] [CrossRef]
  81. Volesky, B.; Holan, Z.R. Biosorption of heavy metals. Biotechnol. Prog. 1995, 11, 235–250. [Google Scholar] [CrossRef] [PubMed]
  82. Khan, M.A.; Rao, R.A.K.; Ajmal, M. Heavy metal pollution and its control through nonconventional adsorbents (1998–2007): A review. J. Int. Environ. Appl. Sci. 2008, 3, 101–141. [Google Scholar]
  83. Dietert, R.R.; Piepenbrink, M.S. Lead and immune function. Crit. Rev. Toxicol. 2006, 36, 359–385. [Google Scholar] [CrossRef] [PubMed]
  84. Wang, C.; Zhang, Y.; Liang, J.; Shan, G.; Wang, Y.; Shi, Q. Impacts of ascorbic acid and thiamine supplementation at different concentrations on lead toxicity in testis. Clin. Chim. Acta 2006, 370, 82–88. [Google Scholar] [CrossRef] [PubMed]
  85. Vaziri, N.D. Mechanisms of lead-induced hypertension and cardiovascular disease. Am. J. Physiol. Heart Circ. Physiol. 2008, 295, H454–H465. [Google Scholar] [CrossRef] [PubMed]
  86. Mason, L.H.; Harp, J.P.; Han, D.Y. Pb neurotoxicity: Neuropsychological effects of lead toxicity. BioMed Res. Int. 2014, 2014. [Google Scholar] [CrossRef] [PubMed]
  87. Pant, N.; Kumar, G.; Upadhyay, A.D.; Patel, D.K.; Gupta, Y.K.; Chaturvedi, P.K. Reproductive toxicity of lead, cadmium, and phthalate exposure in men. Environ. Sci. Pollut. Res. 2014, 21, 11066–11074. [Google Scholar] [CrossRef] [PubMed]
  88. Mancuso, F.; Arato, I.; Lilli, C.; Bellucci, C.; Bodo, M.; Calvitti, M.; Luca, G. Acute effects of lead on porcine neonatal Sertoli cells in vitro. Toxicol. In Vitro 2018, 48, 45–52. [Google Scholar] [CrossRef] [PubMed]
  89. Lee, M.Y.; Bae, O.N.; Chung, S.M.; Kang, K.T.; Lee, J.Y.; Chung, J.H. Enhancement of platelet aggregation and thrombus formation by arsenic in drinking water: A contributing factor to cardiovascular disease. Toxicol. Appl. Pharmacol. 2002, 179, 83–88. [Google Scholar] [CrossRef] [PubMed]
  90. Kapaj, S.; Peterson, H.; Liber, K.; Bhattacharya, P. Human health effects from chronic arsenic poisoning―A review. J. Environ. Sci. Health Part A 2006, 41, 2399–2428. [Google Scholar] [CrossRef] [PubMed]
  91. States, J.C.; Barchowsky, A.; Cartwright, I.L.; Reichard, J.F.; Futscher, B.W.; Lantz, R.C. Arsenic toxicology: Translating between experimental models and human pathology. Environ. Health Perspect. 2011, 119, 1356–1363. [Google Scholar] [CrossRef] [PubMed]
  92. Argos, M.; Ahsan, H.; Graziano, J.H. Arsenic and human health: Epidemiologic progress and public health implications. Rev. Environ. Health 2012, 27, 191–195. [Google Scholar] [CrossRef] [PubMed]
  93. Naujokas, M.F.; Anderson, B.; Ahsan, H.; Aposhian, H.V.; Graziano, J.H.; Thompson, C.; Suk, W.A. The broad scope of health effects from chronic arsenic exposure: Update on a worldwide public health problem. Environ. Health Perspect. 2013, 121, 295–302. [Google Scholar] [CrossRef] [PubMed]
  94. Duruibe, J.O.; Ogwuegbu, M.O.C.; Egwurugwu, J.N. Heavy metal pollution and human biotoxic effects. Int. J. Phys. Sci. 2007, 2, 112–118. [Google Scholar]
  95. Martin, S.; Griswold, W. Human health effects of heavy metals. Environ. Sci. Technol. Br. Citizens 2009, 15, 1–6. [Google Scholar]
  96. Bernard, A. Cadmium & its adverse effects on human health. Indian J. Med. Res. 2008, 128, 557–564. [Google Scholar] [PubMed]
  97. Karri, V.; Kumar, V.; Ramos, D.; Oliveira, E.; Schuhmacher, M. Comparative In Vitro Toxicity Evaluation of Heavy Metals (Lead, Cadmium, Arsenic, and Methylmercury) on HT-22 Hippocampal Cell Line. Biol. Trace Elem. Res. 2017. [Google Scholar] [CrossRef] [PubMed]
  98. Costa, M.; Klein, C.B. Toxicity and carcinogenicity of chromium compounds in humans. Crit. Rev. Toxicol. 2006, 36, 155–163. [Google Scholar] [CrossRef] [PubMed]
  99. Gaetke, L.M.; Chow, C.K. Copper toxicity, oxidative stress, and antioxidant nutrients. Toxicol. 2003, 189, 147–163. [Google Scholar] [CrossRef]
  100. Uriu-Adams, J.Y.; Keen, C.L. Copper, oxidative stress, and human health. Mol. Asp. Med. 2005, 26, 268–298. [Google Scholar] [CrossRef] [PubMed]
  101. Gosens, I.; Cassee, F.R.; Zanella, M.; Manodori, L.; Brunelli, A.; Costa, A.L.; Stone, V. Organ burden and pulmonary toxicity of nano-sized copper (II) oxide particles after short-term inhalation exposure. Nanotoxicology 2016, 10, 1084–1095. [Google Scholar] [CrossRef] [PubMed]
  102. Jan, A.T.; Azam, M.; Siddiqui, K.; Ali, A.; Choi, I.; Haq, Q.M.R. Heavy metals and human health: Mechanistic insight into toxicity and counter defense system of antioxidants. Int. J. Mol. Sci. 2015, 16, 29592–29630. [Google Scholar] [CrossRef] [PubMed]
  103. Lamaia, C.; Kruatrachuea, M.; Pokethitiyooka, P.; Upathamb, E.S.; Soonthornsarathoola, V. Toxicity and accumulation of lead and cadmium in the filamentous green alga Cladophora fracta (OF Muller ex Vahl) Kutzing: A laboratory study. Sci. Asia 2005, 31, 121–127. [Google Scholar] [CrossRef]
  104. Godlewska-Żyłkiewicz, B. Analytical applications of living organisms for preconcentration of trace metals and their speciation. Crit. Rev. Anal.Chem. 2001, 31, 175–189. [Google Scholar] [CrossRef]
  105. Arief, V.O.; Trilestari, K.; Sunarso, J.; Indraswati, N.; Ismadji, S. Recent progress on biosorption of heavy metals from liquids using low cost biosorbents: Characterization, biosorption parameters and mechanism studies. CLEAN–Soil Air Water 2008, 36, 937–962. [Google Scholar] [CrossRef]
  106. Monteiro, C.M.; Castro, P.M.; Malcata, F.X. Metal uptake by microalgae: Underlying mechanisms and practical applications. Biotechnol. Prog. 2012, 28, 299–311. [Google Scholar] [CrossRef] [PubMed]
  107. Wilde, K.L.; Stauber, J.L.; Markich, S.J.; Franklin, N.M.; Brown, P.L. The effect of pH on the uptake and toxicity of copper and zinc in a tropical freshwater alga (Chlorella sp.). Arch. Environ. Contam. Toxicol. 2006, 51, 174–185. [Google Scholar] [CrossRef] [PubMed]
  108. Kaplan, D. Absorption and adsorption of heavy metals by microalgae. In Handbook of Microalgal Culture: Applied Phycology and Biotechnology, 2nd ed.; John Wiley & Sons, Ltd.: New York, NY, USA, 2013; Chapter 32; pp. 602–611. [Google Scholar]
  109. Gupta, V.K.; Rastogi, A. Equilibrium and kinetic modelling of cadmium (II) biosorption by nonliving algal biomass Oedogonium sp. from aqueous phase. J. Hazard. Mater. 2008, 153, 759–766. [Google Scholar] [CrossRef] [PubMed]
  110. Mehta, S.K.; Gaur, J.P. Use of algae for removing heavy metal ions from wastewater: Progress and prospects. Crit. Rev. Biotechnol. 2005, 25, 113–152. [Google Scholar] [CrossRef] [PubMed]
  111. Perales-Vela, H.V.; Pena-Castro, J.M.; Canizares-Villanueva, R.O. Heavy metal detoxification in eukaryotic microalgae. Chemosphere 2006, 64, 1–10. [Google Scholar] [CrossRef] [PubMed]
  112. Schiewer, S.; Volesky, B. Biosorption by marine algae. In Bioremediation; Springer: Dordrecht, The~Netherlands, 2000; pp. 139–169. [Google Scholar]
  113. Romera, E.; Gonzalez, F.; Ballester, A.; Blazquez, M.L.; Munoz, J.A. Biosorption with algae: A statistical review. Crit. Rev. Biotechnol. 2006, 26, 223–235. [Google Scholar] [CrossRef] [PubMed]
  114. Bhatnagar, A.; Sillanpää, M. Applications of chitin-and chitosan-derivatives for the detoxification of water and wastewater—A short review. Adv. Colloid Int. 2009, 152, 26–38. [Google Scholar] [CrossRef] [PubMed]
  115. Filipič, M. Mechanisms of cadmium induced genomic instability. Mutat. Res./Fund. Mol. Mech. Mutagen. 2012, 733, 69–77. [Google Scholar] [CrossRef] [PubMed]
  116. Demim, S.; Drouiche, N.; Aouabed, A.; Benayad, T.; Dendene-Badache, O.; Semsari, S. Cadmium and nickel: Assessment of the physiological effects and heavy metal removal using a response surface approach by L. gibba. Ecol. Eng. 2013, 61, 426–435. [Google Scholar] [CrossRef]
  117. Sbihi, K.; Cherifi, O.; El Gharmali, A.; Oudra, B.; Aziz, F. Accumulation and toxicological effects of cadmium, copper and zinc on the growth and photosynthesis of the freshwater diatom Planothidium lanceolatum (Brébisson) Lange-Bertalot: A laboratory study. J. Mater. Environ. Sci. 2012, 3, 497–506. [Google Scholar]
  118. Bădescu, I.S.; Bulgariu, D.; Bulgariu, L. Alternative utilization of algal biomass (Ulva sp.) loaded with Zn (II) ions for improving of soil quality. J. Appl. Phycol. 2017, 29, 1069–1079. [Google Scholar] [CrossRef]
  119. Cheng, J.; Yin, W.; Chang, Z.; Lundholm, N.; Jiang, Z. Biosorption capacity and kinetics of cadmium (II) on live and dead Chlorella vulgaris. J. Appl. Phycol. 2017, 29, 211–221. [Google Scholar] [CrossRef]
  120. Mirghaffari, N.; Moeini, E.; Farhadian, O. Biosorption of Cd and Pb ions from aqueous solutions by biomass of the green microalga, Scenedesmus quadricauda. J. Appl. Phycol. 2015, 27, 311–320. [Google Scholar] [CrossRef]
  121. Lupea, M.; Bulgariu, L.; Macoveanu, M. Biosorption of Cd(II) from aqueous solution on marine green algae biomass. Environ. Eng. Manag. J. 2012, 11, 607–615. [Google Scholar]
  122. Sarı, A.; Tuzen, M. Biosorption of Pb (II) and Cd (II) from aqueous solution using green alga (Ulva lactuca) biomass. J. Hazard. Mater. 2008, 152, 302–308. [Google Scholar] [CrossRef] [PubMed]
  123. Sarı, A.; Tuzen, M. Biosorption of cadmium (II) from aqueous solution by red algae (Ceramium virgatum): Equilibrium, kinetic and thermodynamic studies. J. Hazard. Mater. 2008, 157, 448–454. [Google Scholar] [CrossRef] [PubMed]
  124. Karthikeyan, S.; Balasubramanian, R.; Iyer, C.S.P. Evaluation of the marine algae Ulva fasciata and Sargassum sp. for the biosorption of Cu (II) from aqueous solutions. Bioresour. Technol. 2007, 98, 452–455. [Google Scholar] [CrossRef] [PubMed]
  125. Bayramoğlu, G.; Tuzun, I.; Celik, G.; Yilmaz, M.; Arica, M.Y. Biosorption of mercury (II), cadmium (II) and lead (II) ions from aqueous system by microalgae Chlamydomonas reinhardtii immobilized in alginate beads. Int. J. Miner. Process. 2006, 81, 35–43. [Google Scholar] [CrossRef]
  126. Gupta, V.K.; Shrivastava, A.K.; Jain, N. Biosorption of chromium (VI) from aqueous solutions by green algae Spirogyra species. Water Res. 2001, 35, 4079–4085. [Google Scholar] [CrossRef]
  127. Kaewsarn, P.; Yu, Q. Cadmium (II) removal from aqueous solutions by pre-treated biomass of marine alga Padina sp. Environ. Pollut. 2001, 112, 209–213. [Google Scholar] [CrossRef]
  128. Matheickal, J.T.; Yu, Q.; Woodburn, G.M. Biosorption of cadmium (II) from aqueous solutions by pre-treated biomass of marine alga Durvillaea potatorum. Water Res. 1999, 33, 335–342. [Google Scholar] [CrossRef]
  129. Atieh, M.A.; Bakather, O.Y.; Tawabini, B.S.; Bukhari, A.A.; Khaled, M.; Alharthi, M.; Fettouhi, M.; Abuilaiwi, F.A. Removal of chromium (III) from water by using modified and nonmodified carbon nanotubes. J. Nanomat. 2010. [Google Scholar] [CrossRef]
  130. Ali, H.; Khan, E.; Sajad, M.A. Phytoremediation of heavy metals—Concepts and applications. Chemosphere 2013, 91, 869–881. [Google Scholar] [CrossRef] [PubMed]
  131. Vaiopoulou, E.; Gikas, P. Effects of chromium on activated sludge and on the performance of wastewater treatment plants: A review. Water Res. 2012, 46, 549–570. [Google Scholar] [CrossRef] [PubMed]
  132. Miretzky, P.; Cirelli, A.F. Cr (VI) and Cr (III) removal from aqueous solution by raw and modified lignocellulosic materials: A review. J. Hazard. Mater. 2010, 180, 1–19. [Google Scholar] [CrossRef] [PubMed]
  133. Hu, J.; Chen, C.; Zhu, X.; Wang, X. Removal of chromium from aqueous solution by using oxidized multiwalled carbon nanotubes. J. Hazard. Mater. 2009, 162, 1542–1550. [Google Scholar] [CrossRef] [PubMed]
  134. Acharya, J.; Sahu, J.N.; Mohanty, C.R.; Meikap, B.C. Removal of lead (II) from wastewater by activated carbon developed from Tamarind wood by zinc chloride activation. Chem. Eng. J. 2009, 149, 249–262. [Google Scholar] [CrossRef]
  135. Cechinel, M.A.P.; de Souza, A.A.U. Study of lead (II) adsorption onto activated carbon originating from cow bone. J. Clean. Prod. 2014, 65, 342–349. [Google Scholar] [CrossRef]
  136. Qu, X.; Alvarez, P.J.; Li, Q. Applications of nanotechnology in water and wastewater treatment. Water Res. 2013, 47, 3931–3946. [Google Scholar] [CrossRef] [PubMed]
  137. Cristian, P.; Violeta, P.; Anita-Laura, R.; Raluca, I.; Alexandrescu, E.; Andrei, S.; Daniela, I.E.; Raluca, M.A.; Cristina, M.; Ioana, C.A. Removal of zinc ions from model wastewater system using bicopolymer membranes with fumed silica. J. Water Process Eng. 2015, 8, 1–10. [Google Scholar] [CrossRef]
Marinedrugs 16 00065 g001 550
Figure 1. Biosorption of potentially toxic elements by an algae cell. Reproduced with modification from [38], with permission from Elsevier.
Figure 1. Biosorption of potentially toxic elements by an algae cell. Reproduced with modification from [38], with permission from Elsevier.
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Figure 2. A schematic representation of the mechanisms involved in the biosorption of potentially toxic elements, e.g., heavy metal ions.
Figure 2. A schematic representation of the mechanisms involved in the biosorption of potentially toxic elements, e.g., heavy metal ions.
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Figure 3. A schematic representation of three classes of metals based on ligands present in biological systems. LCI, ligand class I; LCII, ligand class II; and LCIII, ligand class III.
Figure 3. A schematic representation of three classes of metals based on ligands present in biological systems. LCI, ligand class I; LCII, ligand class II; and LCIII, ligand class III.
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Table
Table 1. Toxic effects and major mechanisms of toxicity of different heavy metals.
Table 1. Toxic effects and major mechanisms of toxicity of different heavy metals.
Heavy MetalMajor Uses/SourcesToxic EffectsMechanism of ToxicityReferences
Lead (Pb)Lead batteries, lead paint, devices to shield from X-rays.Nervous system, male reproductive system, microvascular endothelium, immune system, impairs mammalian spermatogenesis and sperm quality in vivo, inhibits sperm functions in vitro.Lead has no biological functions. Oxidative stress (reactive oxygen species, ROS), with a reduction in the effects of antioxidants, is the principal mechanism. Lead ions also replace other ions such as Ca2+, Mg2+, and Na+ and disturb normal cell functions such as cellular adhesion, apoptosis, and neurotransmitter release.[83,84,85,86,87,88]
Arsenic(Ar)Agricultural chemicals (pesticides, fungicides, herbicides).Cardiovascular/peripheral vascular disease, developmental abnormalities, immunological, and neurological disorders, carcinogenesis, diabetes, portal fibrosis.Oxidative stress, genotoxicity, alteration in DNA repair, and p53 suppression (major contributor to carcinogenesis).[89,90,91,92,93]
Cadmium (Cd)Metal industry, paint pigments, fertilizers, cigarette smoke, food.Pulmonary and gastrointestinal irritation, carcinogenesis (development of adenocarcinomas), Kidneys, liver and bones are also effected by cadmium exposure.Competition with other ions (zinc, iron, copper), genotoxicity, lipid peroxidation, oxidative stress.[94,95,96,97]
Chromium
Cr(III)/Cr (VI)		Anticorrosive, industrial welding, chrome plating, leather industry, wood preservation. Carcinogenic, gastric and intestinal ulcers, sperm damage, male reproductive system problems, anemia.Cr (VI) is more potent than Cr (III); Oxidative stress, genotoxicity, alteration in cellular signaling pathway[94,98]
Mercury (Hg)Natural processes involved oceanic emissions and biomass burning. Anthropogenic sources included power plants, metal industry and gold mining.Alzheimer’s disease, Parkinsonism, respiratory depression Binding of mercury with sulfhydryl (–SH) groups disrupts normal cellular enzymatic processes. Increase in free radical concentration due to blockage of GSH by Hg is responsible for cell-damaging effects.[94,95,97]
Copper (Cu)Agriculture (fertilizers), leather industry (tanning), and photo-voltaic cells.Carcinogenic, neurodegenerative disorders, responsible for complications in diabetes, promotes atherosclerosis.Oxidative stress, enzyme inhibition, replaces normal ions of the body.[94,99,100,101]
Zinc (Zn)Oil refinery, mining, brass manufacturing, plumbing.Ataxia, depression, gastrointestinal irritation, hematuria, icterus, impotence, kidney and liver failure, lethargy, macular degeneration, metal fume fever, prostate cancer, seizures, vomiting.[94,102]
Table
Table 2. Biosorption potentialities of various marine algae to remove potentially toxic elements from aqueous solutions.
Table 2. Biosorption potentialities of various marine algae to remove potentially toxic elements from aqueous solutions.
Potentially Toxic Elements Algae UsedAdsorption CapacityReferences
Zn(II)Ulva sp.29.63 mg/g[118]
Cd(II)Chlorella vulgaris (dead)96.8%[119]
Cd(II)Chlorella vulgaris (live)95.2%[119]
CdScenedesmus quadricauda66%[120]
PbScenedesmus quadricauda82%[120]
Cd(II)Ulva lactuca85%[121]
Cd(II)Ulva lactuca29.2 mg/g[122]
Pb(II)Ulva lactuca34.7 mg/g[122]
Cd(II)Ceramium virgatum39.7 mg/g[123]
Cu(II)Ulva fasciata73.5 mg/g[124]
Cu(II)Sargassum sp.72.5 mg/g[124]
Hg(II)Chlamydomonas reinhardtii89.5 mg/g[125]
Cd(II)Chlamydomonas reinhardtii66.5 mg/g[125]
Pb(II)Chlamydomonas reinhardtii253.6 mg/g[125]
Cr(VI)Spirogyra sp.14.7 × 103 mg metal/kg[126]
Cd(II)Padina sp.90%[127]
Cd(II)Durvillaea potatorum90%[128]

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Bilal, M.; Rasheed, T.; Sosa-Hernández, J.E.; Raza, A.; Nabeel, F.; Iqbal, H.M.N. Biosorption: An Interplay between Marine Algae and Potentially Toxic Elements—A Review. Mar. Drugs 2018, 16, 65. https://doi.org/10.3390/md16020065

AMA Style

Bilal M, Rasheed T, Sosa-Hernández JE, Raza A, Nabeel F, Iqbal HMN. Biosorption: An Interplay between Marine Algae and Potentially Toxic Elements—A Review. Marine Drugs. 2018; 16(2):65. https://doi.org/10.3390/md16020065

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Bilal, Muhammad, Tahir Rasheed, Juan Eduardo Sosa-Hernández, Ali Raza, Faran Nabeel, and Hafiz M. N. Iqbal. 2018. "Biosorption: An Interplay between Marine Algae and Potentially Toxic Elements—A Review" Marine Drugs 16, no. 2: 65. https://doi.org/10.3390/md16020065

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