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Article

The Catalytic Activity of Biosynthesized Magnesium Oxide Nanoparticles (MgO-NPs) for Inhibiting the Growth of Pathogenic Microbes, Tanning Effluent Treatment, and Chromium Ion Removal

by
Ebrahim Saied
1,
Ahmed M. Eid
1,
Saad El-Din Hassan
1,*,
Salem S. Salem
1,
Ahmed A. Radwan
1,
Mahmoud Halawa
2,
Fayez M. Saleh
3,
Hosam A. Saad
4,
Essa M. Saied
5,6 and
Amr Fouda
1,*
1
Department of Botany and Microbiology, Faculty of Science, Al-Azhar University, Nasr City, Cairo 11884, Egypt
2
SAJA Pharmaceuticals, 6th of October, Giza 12573, Egypt
3
Department of Medical Microbiology, Faculty of Medicine, University of Tabuk, Tabuk 71491, Saudi Arabia
4
Department of Chemistry, College of Science, Taif University, P.O. Box 11099, Taif 21944, Saudi Arabia
5
Chemistry Department, Faculty of Science, Suez Canal University, Ismailia 41522, Egypt
6
Institute for Chemistry, Humboldt Universität zu Berlin, Brook-Taylor-Str. 2, 12489 Berlin, Germany
*
Authors to whom correspondence should be addressed.
Catalysts 2021, 11(7), 821; https://doi.org/10.3390/catal11070821
Submission received: 28 June 2021 / Revised: 4 July 2021 / Accepted: 5 July 2021 / Published: 6 July 2021
(This article belongs to the Special Issue Recent Advances on Nano-Catalysts for Biological Processes)
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Versions Notes

Abstract

:
Magnesium oxide nanoparticles (MgO-NPs) were synthesized using the fungal strain Aspergillus terreus S1 to overcome the disadvantages of chemical and physical methods. The factors affecting the biosynthesis process were optimized as follows: concentration of Mg(NO3)2·6H2O precursor (3 mM), contact time (36 min), pH (8), and incubation temperature (35 °C). The characterization of biosynthesized MgO-NPs was accomplished using UV-vis spectroscopy, Fourier transform infrared (FT-IR) spectroscopy, transmission electron microscopy (TEM), scanning electron microscopy—energy dispersive X-ray (SEM-EDX), X-ray diffraction (XRD), and dynamic light scattering (DLS). Data confirmed the successful formation of crystallographic, spherical, well-dispersed MgO-NPs with a size range of 8.0–38.0 nm at a maximum surface plasmon resonance of 280 nm. The biological activities of biosynthesized MgO-NPs including antimicrobial activity, biotreatment of tanning effluent, and chromium ion removal were investigated. The highest growth inhibition of pathogenic Staphylococcus aureus, Bacillus subtilis, Pseudomonas aeruginosa, Escherichia coli, and Candida albicans was achieved at 200 μg mL–1 of MgO-NPs. The biosynthesized MgO-NPs exhibited high efficacy to decolorize the tanning effluent (96.8 ± 1.7% after 150 min at 1.0 µg mL–1) and greatly decrease chemical parameters including total suspended solids (TSS), total dissolved solids (TDS), biological oxygen demand (BOD), chemical oxygen demand (COD), and conductivity with percentages of 98.04, 98.3, 89.1, 97.2, and 97.7%, respectively. Further, the biosynthesized MgO-NPs showed a strong potential to remove chromium ions from the tanning effluent, from 835.3 mg L–1 to 21.0 mg L–1, with a removal percentage of 97.5%.

1. Introduction

Environmental and water pollution dramatically increase due to industrial development, populational growth, and energy production [1]. These pollutants are considered the main factors for disease, illness, and death due to their toxicity, non-degradability, and tendency to accumulate in the food chain [2]. The different industrial activities are the main sources of contaminated wastewater because they produce highly toxic waste that has a long-term negative impact [3,4]. The tannery and leather sectors are considered the largest industries that use hazardous chemical compounds and require a high amount of water [5]. These sectors produce high amounts of effluents containing highly toxic compounds and are characterized by increase total dissolved solids (TDS), total suspended solids (TSS), conductivity, chemical oxygen demand (COD), and biochemical oxygen demand (BOD) [6]. Therefore, the tanning and leather effluents require extra treatment before discharge into the eco-system. Chromium is considered one of the most widely used heavy metals in the tanning and leather industry and is widely discharged as part of the effluent [7]. Further, chromium is incorporated into electroplating and paint manufacturing, resulting in large quantities being discharged into the environment [8]. Moreover, the development of new compounds to overcome the resistance properties of microbes to different antibiotic is the main goal for investigators [9,10].
Nanotechnology sciences provide a promising tool for the synthesis of new active compounds with superior properties to be breakthrough applications in various biomedical and biotechnological sectors [11,12]. Among these new nanoparticles, magnesium oxide nanoparticles (MgO-NPs) are characterized by excellent optical, thermal, mechanical, and chemical properties [13]. MgO-NPs have high reactivity due to the presence of highly reactive edges and a high surface area [14]. Therefore, MgO-NPs have a variety of applications in various fields such as catalyst supports, agricultural products, paints, superconductor products, antimicrobial materials, photonic devices, sensors, and adsorbents [15,16,17]. Notably, MgO-NPs have antibacterial properties against harmful microbes, for instance, S. aureus and E. coli [18,19]. Further, they can be utilized as adsorbent materials due to the high removal efficiency [20]. MgO-NPs act as excellent adsorbents for various chemical species and this property increases with a decrease in MgO size [21]. Recently, MgO nanoparticles have obtained popularity in environmental science due to their fascinating and intrinsic properties [22].
Several chemical and physical methods have been used to fabricate MgO-NPs such as chemical precipitation, thermal decomposition, sol-gel, combustion, and chemical vapor deposition [13,23]. These methods predominantly require several processing steps, controlled pH, high temperature and pressure, expensive equipment, and toxic chemicals. These techniques produce numerous by-products that may be toxic to ecosystems. Therefore, there is a need to develop a low-cost, eco-friendly method for nanoparticle synthesis [11]. Recently, the biogenic synthesis of NPs has a wide range of interest because of the reduction or elimination of toxic substances that are present in the environment from chemical and physical methods [24]. Microorganisms such as fungi, yeast, actinomycetes, and bacteria can reduce metal and their oxides to NPs. The biogenic synthesis of NPs using fungi (eukaryotic organisms) has numerous advantages over the prokaryotic organisms, e.g., easy to multiply, grow, handle, and downstream process for nano-biosynthesis [25].
In the present study, we have tried to explore a rapid, cost-effective, eco-friendly method for fabricating MgO-NPs using the fungal strain Aspergillus terreus S1. The optimized biosynthesis process was investigated by studying the effect of metal precursors, incubation temperature, pH, and contact time. The biogenically synthesized MgO-NPs were characterized using various techniques consisting of UV-vis spectroscopy, X-Ray diffraction (XRD), scanning and energy dispersive X-Ray spectroscopy (SEM-EDX), transmission electron microscopes (TEM), dynamic light scattering (DLS), and Fourier-transform infrared spectroscopy (FT–IR). The efficacy of biosynthesized MgO-NPs to inhibit the growth of different pathogenic bacterial and fungal strains was assessed. Moreover, utilizing MgO-NPs for decolorization and treatment of tanning effluent and removal of heavy metals are among the main goals.

2. Results and Discussion

2.1. Isolation and Identification of the Fungal Isolates

In the current study, five fungal isolates were obtained from cultivated soil samples; we selected fungal isolate S1 for MgO-NPs based on its best and rapid NP synthesis. The selected fungal isolate underwent primary identification using morphological and microscopic analysis. Original identification was done according to standard keys based on morphological and cultural characteristics. The fungal isolate appears brownish, with compact conidial heads, biseriate, and densely columnar. Conidiophores are smooth and hyaline. The conidia are small, about 2 μm in diameter, globose-shaped, and smooth-walled. According to morphological and cultural characterization, the fungal isolate S1 belongs to Aspergillus sp. [26,27]. The primary identification was confirmed by amplification and sequencing of the internal transcribed spacer (ITS) gene. The sequence analysis revealed that the fungal strain S1 is strongly related to Aspergillus terreus (accession number: MT558939) with a similarity percentage of 93%. The fungal strain obtained in this study was identified as Aspergillus terreus strain S1 (Figure 1). The sequence analysis acquired from the current study was deposit in GenBank under accession number MW774586.
Aspergillus terreus has been characterized by its high secretion of various secondary metabolites such as chemicals (i.e., terrein, terreic acid, and terretonin), enzymes (Lipase, amylase, and reductase), fermentative compounds (i.e., polyketide compounds), and a wide range of by-products [28,29,30]. These various metabolites enable faster incorporation of A. terreus into various biotechnological applications. Therefore, we can benefit from these metabolites in the green synthesis of metal and metal oxide nanoparticles. Interestingly, A. terreus was utilized as a biocatalyst for the green synthesis of zinc, titanium, and magnesium nanoparticles [31].

2.2. Biogenic Synthesis of MgO-NPs

Metal and metal oxide nanoparticle synthesis by biological approaches can be used as an alternative to chemical and physical methods [32]. This phenomenon can be attributed to the advantages of biological synthesis such as the cost, the environmentally friendly nature, biocompatibility, scalability, and the avoidance of harsh synthesis conditions such as high temperature and pH [11]. Among biological entities, fungi can be identified as a promising tool for biogenic nanoparticle synthesis because of diverse metabolites and high metal tolerances [33]. Proteins and enzymes secreted by A. terreus strain S1 have an important role in the reduction of Mg(NO3)2·6H2O to MgO-NPs and confer capping and stabilization features [31,34].
The initial observation for successful MgO-NP production is the color change from colorless to turbid white after stirring Mg (NO3)2·6H2O with biomass filtrate. This change can be attributed to the role of A. terreus-secreted metabolites in the reduction of NO3– to NO2 and then the reduction of Mg2+ to Mg(OH)2 by liberated electrons. The as-formed Mg(OH)2 was calcinated at 400 °C to form MgO-NPs [35].
The production of MgO-NPs was confirmed by measuring the maximum surface plasmon resonance (SPR) by UV-Vis spectroscopy. The morphological characteristics (size and shape), as well as distribution of biogenically synthesized NPs, are usually correlated with SPR [36]. In this respect, Nguyen et al. [37] reported that the size of biogenic MgO-NPs was smaller or larger according to 300 ≤ SPR ≥ 300. In the current study, the maximum SPR value of biogenic MgO-NPs was detected at a wavelength of 280 nm (Figure 2), which confirms the formation of particles at the nanoscale. Further, the MgO-NPs synthesized by different extracts (flower, bark, leaf) of Tecoma stans (L.) showed maximum SPR peaks at 281 nm [37]. Moreover, the maximum absorption band of MgO-NPs synthesized by the floral extract of Matricaria chamomilla L. was observed at 230 nm [38].

2.3. Optimizing Biosynthesized MgO-NPs

The stability and biological activity of biogenic nanoparticles are usually influenced by environmental factors such as precursor concentration, contact time or incubation time, pH values, and incubation temperature. The investigated factors have various impacts on fungal-secreted metabolites such as enzymes, proteins, carbohydrates, and hence the reducing and stabilizing processes are affected [39]. Therefore, the optimization of these environmental factors will decrease the times required for biosynthesis, increase the NP stability, reduce the NP agglomeration, and finally support the productivity [40].
The activity of reducing agents differs according to the metal precursor concentration. In the current study, the absorbance band at λmax280 was increased by increasing the precursor concentration, and the maximum absorbance was achieved at 3 mM. By increasing the Mg(NO3)2·6H2O concentration up to 3 mM, the absorbance was decreased (Figure 3A). According to obtained data, the fungal metabolites exhibited the optimum reduction of the metal precursor at 3 mM, whereas above and below this concentration, the biosynthesized MgO-NPs aggregated and hence decreased the absorbance band [41]. Muangban and Jaroenapiba [42] reported that tungsten oxide nanofibers tended to agglomerate by increasing the metal precursor concentration because of increasing nanoparticle size. Further, Jeevanandam et al. [43] study the effect of Mg(NO3)2·6H2O concentration on the average particle size of MgO-NPs synthesized by Aloe barbadensis aqueous extract. It can be concluded that an increase in the concentration of the metal precursor leads to increased nanoparticle size and hence an increase in NP aggregation.
The contact time or reaction time between the fungal biomass filtrate and optimum Mg(NO3)2·6H2O concentration (3 mM) is considered a critical factor affecting the biogenic synthesis of MgO-NPs. The intensity of the color that formed was monitored by detecting the maximum absorbance band at λmax280. Data illustrated in Figure 3B show that the optimum contact time between the metal precursor and fungal biomass filtrate was 36 min. At this time, the maximum color intensity was achieved because a large number of metal ions were reduced. On the other hand, the absorbance intensity was decreased by increasing contact time due to the aggregation of some MgO-NPs, and then the color intensity and particle size were reduced. Moreover, in the early contact time stages, the low number of metal ions was reduced and hence the SPR peak appeared broader [44,45]. Compatible with our study, the optimum contact time for the biogenic synthesis of MgO-NPs by Aloe barbadensis plant extract was 30 min [43]. Synthesis by chemical and physical methods such as microemulsion, sol-gel, co-precipitation, and solvothermal methods required a contact time of more than 48 min [46].
The effect of different pH values ranging between 6 and 11 on the biogenic synthesis of MgO-NPs by Aspergillus terreus strain S1 was shown (Figure 3C). Data analysis showed that the highest absorbance at λmax280 was accomplished at pH 8, which is evidence of maximum MgO-NP production. This behavior could be attributed to the stabilizing fungal metabolites including proteins and enzymes secreted by Aspergillus terreus strain S1 in an alkaline medium [47]. The metabolites present in the biomass filtrate of A. carbonarious D-1 were more active to reduce FeCl3·6H2O and Mg(NO3)2.6H2O to fabricate α-Fe2O3-NPs and MgO-NPs in an alkaline medium [48].
The activity of reducing agents involved in the biomass filtrate of A. terreus strain S1 is correlated with the incubation temperature. Therefore, it is important to detect the optimum temperature required for reducing, capping, and stabilizing MgO-NPs. In the current study, the effects of different incubation temperatures (25–40 °C) on the color intensity and hence biogenic MgO-NPs synthesis were investigated. Data showed that the metabolites involved in the A. terreus biomass filtrate were highly active as reducing agents at 35 °C (Figure 3D). The absorbance intensity was decreased at a temperature of more or less than 35 °C. This was attributed to the enzymes and proteins being more stable at this temperature. Hassan et al. [41] reported that the biomass filtrate of Rhizopus oryaze was more stable at an incubation temperature of 35 °C during MgO nanoparticle synthesis. Moreover, the size, shape, and stability of nanoparticles are correlated with the incubation temperature [43]. Interestingly, increasing the incubation temperature will lead to a higher diffusion coefficient, which decreases the reaction time needed to form stable particles and hence decreases the induction time [49].

2.4. Characterizations of Biogenically Synthesized MgO-NPs

2.4.1. Fourier Transform Infrared (FT-IR) Spectroscopy

FT-IR analysis is a powerful technique used for identifying the possible functional groups in the biomass filtrate of A. terreus strain S1 that are responsible for the reduction of metal precursors to form MgO-NPs [50]. FT-IR analysis scans at a wavenumber between 400 to 4000 cm–1 as shown in Figure 4. The result showed that several intense absorption peaks appeared at 3700, 3420, 2850, 2727, 2398, 1630, 1370, 1027, and 520 cm−1. The peak observed at 3700 cm–1 signifies the –OH stretching band [51]. The broad peak at 3420 cm–1 corresponds to hydrogen bonds arising from NH2 and OH groups in protein molecules [52]. The peaks observed at 2850, 2727, and 2398 cm–1 may correspond to the C-H stretching of methylene groups of proteins. The medium peaks observed at 1630 cm–1 correspond to the bending mode of primary amine (N―H) overlapped with either amide or carboxylate salt. The medium peak at 1370 cm–1 can be related to C–H bending vibrations of the aromatic tertiary amine group [53,54], whereas the peak at 1027 cm–1 matched the Mg–OH stretching [55] with the C-H out-of-plane bend. The peaks that appear between wavenumber 400–700 cm–1 confirm the presence of MgO at the nanoscale [51,53,56]. The peaks observed in FT-IR spectra reflect the capacity of metabolites present in the A. terreus strain S1 biomass filtrate to reduce, cap, and stabilize MgO-NPs.

2.4.2. Transmission Electron Microscopy

TEM analysis was carried out to determine the approximate size and shape of the A. terreus-mediated MgO-NPs biosynthesized. Data illustrated in Figure 5A showed that the biogenic MgO-NPs synthesized by harnessing metabolites of A. terreus strain S1 had a spherical shape and well-dispersed narrow-sized particles surrounded with capping proteins and enzymes. TEM image measurement revealed that the sizes of biogenic MgO-NPs ranged between 8.0 and 38.0 nm with an average diameter of 19.91 ± 9.9 nm (Figure 5B). In our recent study, Aspergillus carbonarious D-1 mediated green synthesis of spherical MgO-NPs with an average size of 20–80 nm [48]. Compatible with our study, the particle size of spherical MgO-NPs synthesized by Aspergillus terreus TFR was 10 nm with a PDI value of 0.236 and 100% conversion of the precursor compound into nanoparticles [31]. Moreover, the plant extract of Pisidium guvajava and Aloe vera mediated biosynthesis of MgO-NPs with an average size range of 50 nm [57]. It is well known from previously published studies that the biological activity of NPs is increased by decreasing the average size [58,59]. The growth inhibition percentages of Bacillus subtilis after treatment with different sizes of biosynthesized MgO-NPs (35.9 nm, 47.3 nm, and micron size 2145.9 nm) were 96.1%, 94.5%, and 75.7%, respectively [60]. In this study, the size of fabricated MgO-NPs was small (8.0–39.0 nm), and we therefore predicted their integration in different biomedical and biotechnological applications.

2.4.3. Scanning Electron Microscopy—Energy Dispersive X-ray (SEM-EDX)

The SEM-EDX analysis is considered a useful technique to study the topographical structure of biosynthesized MgO-NPs, aggregation, and chemical compositions. As seen in Figure 6A the MgO-NPs synthesized by A. terreus strain S1 were well-dispersed and spherical. Moreover, the presence of Mg and O ions in the sample was confirmed by the EDX profile. Data showed that the weight percentages of Mg and O were 18.3% and 28.1%, respectively, whereas the atomic percentages were 10.9% and 25.8%, respectively (Figure 6B). Further, the successful fabrication of MgO-NPs was confirmed by the presence of a Mg peak at an energy of 0.5 to 1.5 KeV [53] as shown in Figure 6B.
On the other hand, other elements, C, Cl, and Ca, in the MgO-NP sample were detected by EDX profiles with weight percentages of 50.6%, 2.49%, and 0.71%, respectively. The presence of these additional peaks indicates the presence of some impurities in the sample, which was confirmed by XRD analysis. Some investigators attributed the presence of additional peaks in the EDX profile to the hydrolysis of enzymes, proteins, and other fungal metabolites that act as capping and stabilizing agents by X-ray [61].

2.4.4. X-ray Diffraction (XRD) Analysis

The crystallographic structure of optimized MgO-NPs was studied using XRD analysis. XRD spectra (Figure 7A) showed major five intense peaks at 2θ values of 36.94° (111), 42.68° (200), 62.4° (220), 74.28° (311), and 78.62° (222). The identified diffraction peaks matched well with the crystallographic structure according to JCPDS standard (JCPDS file No. 89-7746) [62]. The presence of fine additional peaks in XRD spectra confirms data obtained by EDX analysis, i.e., the sample contained some impurities. According to XRD spectra, oxides represented by Mg(OH)2 and MgO existed in the biosynthesized sample. The observed peaks at 2θ° of 36.9° (111), 75.08° (311), and 78.64° (222) corresponded to Mg(OH)2, whereas, the diffraction peaks at 2θ° of 42.16° (200), and 62.6° (220) signified cubic MgO-NPs [37]. The average crystallite size can be calculated according to XRD analysis using the Debye–Scherrer equation, which was found to be <20 nm.

2.4.5. Dynamic Light Scattering (DLS)

The DLS technique is used to investigate the size and dispersion of MgO-NPs in the colloidal solution through a reaction of light beams with biogenically synthesized MgO-NPs [63]. In the current study, the average size of biogenic MgO-NPs was 40.6 nm, 60.1 nm, and 5.6 nm for volume intensities of 10%, 81.3%, and 8.7% of the colloidal solution (Figure 7B). As shown from the DLS analysis, the size of MgO-NPs was larger than that acquired from other techniques such as TEM and XRD. This is attributed to the coating agent that capped and stabilized the surface of NPs [64,65]. Furthermore, the larger size from DLS may be due to the non-homogenous NP distribution in colloidal solution [66]. Moreover, the Solvation spheres around the nanoparticles may be a factor for the size increase.
The polydispersity index (PDI) refers to the homogeneity percentages of NPs in the colloidal solution. The homogeneity percentages are increased or decreased when the PDI value is lower than or higher than 0.4, respectively. On the other hand, the NP colloidal solution is heterogenous when the PDI value ≥ 1. The obtained data demonstrated that the PDI value of MgO-NPs synthesized by the A. terreus strain S1 was 0.2, which indicates the high homogeneity of the colloidal solution.

2.5. Antimicrobial Activity

The activity of biogenically synthesized MgO-NPs to inhibit the growth of pathogenic Gram-positive bacteria represented by Staphylococcus aureus, Bacillus subtilis, Gram-negative bacteria including Pseudomonas aeruginosa, and Escherichia coli, and unicellular fungi of Candida albicans was studied by the agar well-diffusion method. Analysis of variance showed that the antimicrobial activity of MgO-NPs against selected pathogenic microbes was dependent on the concentration; the activity increased by increasing the NP concentration. The obtained data are compatible with published investigations about the relationship between the activity of NPs and their concentrations [57,59,67]. Results showed that the biogenic MgO-NPs synthesized by A. terreus strain S1 exhibited antimicrobial activity at 200 μg mL–1 against all tested pathogenic microbes as follows: C. albicans (12.8 ± 0.3 mm), E. coli (11.3 ± 0.6 mm), P. aeruginosa (14.7 ± 1.9 mm), S. aureus (11.3 ± 0.6 mm), and B. subtilis (13.3 ± 1.9 mm) (Figure 8). Recently, MgO-NPs synthesized by Rhizopus oryaze E3 showed antimicrobial activity with varied ZOIs, e.g., B. subtilis (11.5 ± 0.5 mm), S. aureus (10.6 ± 0.4 mm), E. coli (14.3 ± 0.7 mm), P. aeruginosa (13.7 ± 0.5 mm), and C. albicans (14.7 ± 0.6 mm) at a concentration of 200 μg mL–1 [41]. Moreover, a Swertia chirayaita plant extract mediated the green synthesis of MgO-NPs with antibacterial activity against S. aureus, E. coli, and S. epidermidis, with ZOIs of 14, 15, and 12 mm, respectively [18].
The minimum inhibitory concentration (MIC) is defined as the lowest concentration of an active substance that inhibits microbial growth. It is important to detect MIC values for active compounds against pathogenic microbes especially if these compounds are integrated into biomedical applications. To achieve this goal in the current study, the activity of different concentrations (150, 100, 50, and 25 μg mL–1) of MgO-NPs was investigated. Data analysis showed that the MIC value for P. aeruginosa was 50 μg mL–1 with a ZOI of 8.3 ± 0.3 mm, whereas E. coli, C. albicans, S. aureus, and B. subtilis had an MIC value of 100 μg mL–1 with ZOIs of 8.0 ± 0.0, 8.7 ± 0.9, 8.0 ± 0.0, and 9.3 ± 0.6 mm, respectively (Figure 8).
The inhibitory effect of biogenic MgO-NPs can be attributed to different mechanisms such as (1) producing reactive oxygen species (ROS), (2) interaction between MgO-NPs and microbial cell walls that ultimately lead to cell death, (3) discharge of Mg2+ ions into the cell, and (4) alkaline effects of MgO on the microbial cell [68,69,70]. In the current study, Gram-negative P. aeruginosa was the most sensitive microorganism toward biosynthesized MgO-NPs, and this phenomenon can be attributed to differences in cell wall structures between Gram-positive and Gram-negative bacteria. The cell wall of Gram-positive bacteria is characterized by a thick layer of peptidoglycan in contrast to Gram-negative bacteria that have a thin layer of peptidoglycan plus lipopolysaccharides (LPS). The positive charge of NPs is strongly attracted to the LPS-negative charge, and hence it is the deposit on the bacterial cell membrane that ultimately disrupts selective permeability [71]. Moreover, MgO-NPs can stop the communication tools, which is quorum sensing between microbial strains, and hence the physiological functions and various microbial activities fail to continue [72,73].

2.6. Biotreatment of Tanning Effluent

The main challenge facing different countries is discovering new active compounds that can be utilized in the treatment of different industrial effluents especially the countries that suffer from water scarcity. Nanotechnology especially that defined as green nanotechnology provides a new approach for producing new active compounds characterized as eco-friendly, with a large surface area, high stability, cost-effectiveness, and hence can be utilized to adsorb different contaminants [74,75]. Among highly contaminated industrial effluent is tanning wastewater, which appears a greenish-blue color because of the presence of chrome ions and other materials at high concentrations [76]. Therefore, the discharge of tanning effluent directly in the surrounding environment without treatment hinders sunlight penetration and hence decreases the pollutant oxidation process [77]. In the current study, the potential of different concentrations (0.25, 0.5, 0.75, and 1.0 µg mL−1) of biogenically synthesized MgO-NPs for treatment of tanning effluent at different interval times (30, 60, 90, 120, 150, 180, and 240 min) was investigated. Data recorded in Table 1 showed that the efficiency of biogenic MgO-NPs to decolorize the tanning effluent was concentration and time-dependent, meaning the decolorization percentages were increased as concentrations and contact time increased. This phenomenon can be attributed to the increase in adsorption sites by increasing the concentration of adsorbents [78]. At the lowest MgO-NP concentration (0.25 µg mL–1), the decolorization percentages ranged from 16.1 ± 1.6% after 30 min contact time to 46.6 ± 3.2% after 240 min as compared to the control (5.8 ± 0.4% after 240 min). At the highest concentration (1.0 µg mL–1), the adsorption sites increased and hence the decolorization increased to reach 89.1 ± 1.6% after 120 min. At this high concentration, the decolorization percentages were not significant at times 150, 180, and 240, i.e., 96.8 ± 1.7%, 97.5 ± 1.6%, and 97.7 ± 1.7% (Table 1, Figure 9). The time and concentration are considered the main factors that should be taken into consideration on a large or industrial scale; therefore, 1.0 µg mL–1 of MgO-NPs and 150 min were chosen as the optimal conditions for decolorization of tanning wastewater and to study the physicochemical parameters that indicate successful treatment.
The successful treatment process by MgO-NPs is monitored by measuring the main factors including pH, BOD, COD, TDS, TSS, and conductivity. These factors are high in tanning effluent due to hazardous chemicals, bicarbonates, calcium phosphates, chlorides, sulfates, nitrates, potassium, sodium, and various dissolved salts [79]. Moreover, the values of these factors are wide-ranging according to the chemicals used, tannery size, type of products, and water used [80]. The alkalinity of crude tanning wastewater is because of high amounts of carbonates and bicarbonates used during tanning steps [81]. Moreover, the high conductivity values of crude wastewater are because of the high content of salts and acids such as sodium and chrome salts. Further, high values of other factors such as TDS, TSS, and conductivity have adverse impacts on plants and aquatic eco-systems [6]. Data recorded in Table 2 showed a high level of measured factors in un-treated tanning effluents as follows: pH (10.5), TSS (8776.3 ± 5.8 mg L–1), TDS (15,720 ± 4.1 mg L–1), BOD (2345.7 ± 7.0 mg L–1), COD (641.7 ± 4.7 mg L–1), and conductivity (26,750.7 ± 6.0 S m–1). MgO-NPs exhibited high efficacy to decrease the factors of tanning effluent as follows: pH (8), TSS (172.0 ± 4.8 mg L–1), TDS (252.0 ± 4.1 mg L–1), BOD (255.0 ± 5.1 mg L–1), COD (18.0 ± 1.9 mg L–1), and conductivity (628.0 ± 3.8 S m–1). As shown, the MgO-NPs can remove BOD, COD, TSS, TDS, and conductivity with percentages of 89.1%, 97.2%, 98.04%, 98.3%, and 97.7%.

2.7. Chromium Ion Removal

Chromium is the main heavy metal released into the environment from different industries such as textiles, electroplating, mining, and fertilizer manufacturing. Leather tanning is considering the main source for discharge of chromium [82]. The toxicity of chromium ions can be attributed to their mutagenic and carcinogenic properties, causing cancer of the lung and digestive tract, nausea, vomiting, diarrhea, epigastric pain, and hemorrhaging [83]. Therefore, there is an urgent need to discover new, high efficacy and eco-friendly adsorption compounds to remove heavy metals. MgO-NPs are characterized by cost-effectiveness, nontoxicity, high adsorption efficacy, abundance, eco-friendly, and biocompatibility [13]. Data represented in Table 2 showed the high efficacy of biogenically synthesized MgO-NPs to decrease the chromium ion concentration from 835.3 ± 2.5 mg L−1 to 21.0 ± 0.7 mg L−1 with a removal percentage of 97.5%. The removal mechanism of heavy metals by MgO-NPs is dependent on precipitation and adsorption, whereas other nanomaterials such as nanotubes, NiO, ZrO2, and TiO2 are dependent on adsorption only [84]. The adsorption process for these nanomaterials is controlled by the size, shape, surface, and textural properties [85]. On the other hand, the dissociation of OH− from the pre-synthesized Mg(OH)2 and the synergistic effects between precipitation and adsorption can be a reason for high MgO-NP adsorption [86]. Another mechanism to explain Cr removal is electrostatic attraction/repulsion [87]. The main Cr form that exists in an aquatic medium at pH > 6.0 is CrO42− [88]. The electrostatic attraction was achieved between the positive charge of NPs and the negative charge on the surface of chromate [89]. In our recent study, MgO-NPs synthesized by harnessing metabolites of Aspergillus niger F1 and Rhizopus oryzae E3 showed removal of Cr from tanning wastewater with percentages of 94.2 ± 1.2% and 95.6 ± 1.6, respectively [41,76]. Therefore, this study provides a new, highly active nanomaterial that has the potential to adsorb various contaminants including heavy metals from tanning effluent and has antimicrobial activity.

3. Materials and Methods

3.1. Reagents and Materials

Chemicals used in the current study including magnesium nitrate hexahydrate (Mg (NO3)2·6H2O) and sodium hydroxide (NaOH) are analytical grade and were obtained from Sigma Aldrich, Cairo, Egypt. Malt Extract agar (MEA) media for fungal isolations and Muller Hinton agar media for antimicrobial activity were readymade (Oxoid, Thermo Fisher Scientific Inc. USA). The tannery wastewater was collected from Robbiki Leather City, 10th of Ramadan, Cairo, Egypt (GPS: N: 30° 17′ 898″, E: 31° 76′ 840″).

3.2. Isolation and Identification of the Fungal Strain

The fungal strain S1 used in the current study for the biosynthesis of MgO-NPs was isolated from a soil sample collected from El-Sharqia Governorate, Egypt (GPS: N: 30°41′588.38″, E: 31°56′211.84″). The isolation procedures were achieved according to Hashem, et al. [90] as follows: 100 µL of the fifth dilution of a diluted soil sample was inoculated onto MEA plates and incubated for 3–4 days at 28 ± 2 °C. All different shapes and colors of fungal colonies were picked and re-inoculated again onto new MEA plates for purification. Finally, the purified colony was preserved on an MEA slant for further work.
The identification was accomplished by routine work including morphological and microscopic characterization. The primary identification was confirmed using internal transcribed spacer (ITS) sequence analysis. The ITS rDNA region was amplified using primers for ITS1 f (5-CTTGGTCATTTAGAGGAAGTAA-3) and ITS4 (5-TCCTCCGCTTATTGATATGC-3) [91]. The PCR mixture contained 1X PCR buffer, 0.5 mM MgCl2, 2.5 U Taq DNA polymerase (QIAGEN, Germantown, MD 20874, USA), 0.25 mM dNTP, 0.5 µL of each primer, and 1 µg of extracted genomic DNA. The PCR was performed in a DNA Engine Thermal Cycler (PTC-200, BIO-RAD, USA) with a program of 94 °C for 3 min, followed by 30 cycles of 94 °C for 30 s, 55 °C for 30 s, and 72 °C for 1 min, followed by a final extension performed at 72 °C for 10 min. The PCR product was checked for the expected sizes on 1% agarose gel and was sequenced by Sigma Company for scientific research, Egypt, with the two primers. The sequence was compared against the GenBank database using the NCBI BLAST tool. Multiple sequence alignment was done using the Clustal Omega software package (https://www.ebi.ac.uk/Tools/msa/clustalo (accessed on 28 June 2021)), and a phylogenetic tree was constructed using the neighbor-joining method with MEGA (Version 6.1) software, with confidence tested by bootstrap analysis (1000 repeats).

3.3. Biogenic Synthesis of MgO-NPs

The fungal biomass filtrate utilized as a biocatalyst for the biogenic synthesis of MgO-NPs was prepared through the inoculation of three disks (0.8 cm in diameter) of fungal strain S1 into 100 mL of malt extract broth (MAB) medium and incubated for five days at 28 ± 2 °C under shaking conditions (150 rpm). At the end of the incubation period, the inoculated MAB medium was centrifuged to collect the fungal biomass. The collected fungal biomass (10 g) was resuspended in 100 mL distilled water for 48 h. at 28 ± 2 °C under shaking conditions. The previous mixture was centrifuged at 15,000 rpm for three minutes; the upper layer (supernatant) was collected and used for biosynthesis of MgO-NPs as follows.
Mg(NO3)2·6H2O (76.6 mg) was dissolved in 10 mL dis. H2O and the volume made to 100 mL by adding 90 mL fungal biomass filtrate to a final concentration of 3 mM. The previous mixture was incubated for 24 h at room temperature. At first, Mg(OH)2 appeared as a turbid white precipitate that was collected and washed with dis. H2O before drying at 100 °C for one hour (Equation (1)). After that, Mg(OH)2 was subjected to calcination at 400 °C for 3 h to form MgO-NPs (Equation (2)) [92].
Mg ( NO 3 ) 2 · 6 H 2 O + H 2 O → Metabolites Fungal Mg ( OH ) 2
Mg ( OH ) 2 → 400 ° C MgO
Optimization factors of MgO-NPs biosynthesis.
The physical and chemical factors affecting the production as well as the distribution of MgO-NPs were optimized. Different factors such as temperature, contact times, different pH values, and Mg (NO3)2·6H2O concentrations are investigated by detecting the maximum surface plasmon resonance by a UV-Vis spectrophotometer (Jenway 6305, Staffordshire, UK). The different contact times (6, 12, 24, 36, 48, and 72 min) between fungal biomass filtrate and Mg (NO3)2·6H2O were assessed. Moreover, the incubation temperatures (25 °C, 30 °C, 35 °C, and 40 °C), different pH values (6, 7, 8, 9, 10, and 11), and different Mg (NO3)2·6H2O concentrations (1–5 mM) were assessed. At the end of each experiment, 1.0 mL of the sample was withdrawn to measure the color intensity at maximum SPR at λmax = 280 nm.

3.4. Characterization of Biosynthesized MgO-NPs

Fourier transform infrared (FT-IR) spectroscopy (Agilent system Cary 660 FT-IR model) was used to inspect the functional groups present in the fungal biomass filtrate and involved in the reduction and stabilization of MgO-NPs. The MgO-NP sample was mixed with KBr and scanned in the range of 400 to 4000 cm‒1.
The physicochemical characterizations of biogenically synthesized MgO-NPs were accomplished using Transmission Electron Microscopy (TEM) (JEOL 1010, Japan, acceleration voltage of 200 KV) to detect the MgO-NP sizes and shapes. A few drops of MgO-NPs suspension were added to the carbon-copper grid, which was subjected to vacuum desiccation before placing on a TEM-holder for analysis [93]. The elemental analysis of biogenically synthesized MgO-NPs was measured using Scanning Electron Microscopy connected to energy dispersive X-rays (SEM-EDX) ((JEOL, JSM-6360LA, Japan). Moreover, the crystallographic structure of MgO-NPs was investigated using X-ray diffraction (XRD) analysis by an X’Pert pro diffractometer (Philips, Eindhoven, Netherlands). The XRD analysis condition was achieved at 2θ values of 4° to 80°, Ni-filtered Cu Ka as an X-ray radiation source, and the operating voltage and current were 40 KV and 30 mA, respectively. Based on XRD analysis, the average size of MgO-NPs was measured using the Debye–Scherrer equation [94] as follows:
D = 0.9 λ / β Cos θ
where D is the average particle size; 0.9 is the Scherrer’s’ constant; λ is the wavelength of X-ray radiation (0.154 nm); β and θ are the half of maximum intensity and Bragg’s angle, respectively.
The size distribution of biogenic MgO-NPs in colloidal solution was detected by dynamic light scattering (DLS) analysis. The sample was subjected to measurement by Zeta sizer nano series (Nano ZS), Malvern, UK.

3.5. Antimicrobial Activity

The efficacy of biogenic MgO-NPs to inhibit the growth of pathogenic Gram-positive bacteria (Bacillus subtilis ATCC 6633 and Staphylococcus aureus ATCC 6538), Gram-negative bacteria (Pseudomonas aeruginosa ATCC 9022 and Escherichia coli ATCC 8739), and unicellular fungi represented by Candida albicans ATCC 10231 was investigated using the agar well-diffusion method. Under aseptic conditions, each bacterial strain was inoculated into Mueller–Hinton agar medium (Oxid, ready-prepared), whereas the unicellular fungi were inoculated into yeast extract peptone dextrose (YEPD) agar medium (containing g L–1:glucose, 20; peptone, 20; yeast extract, 10; agar, 20; distilled water, 1000 mL). Three wells (0.7 cm diameter) were prepared in the inoculated plates and filled with 100 µL of biosynthesized MgO-NPs (200 µg mL−1). Different concentrations of MgO-NPs (150, 100, 50, and 25 µg mL−1) were prepared to detect the minimum inhibitory concentrations (MIC). The plates were kept in the refrigerator for 1.0 h before incubation at 35 ± 2 °C for 24 h. At the end of the incubation period, the diameters of the inhibition zone (ZOI) that appeared around each well were measured in mm [76]. The experiment was carried out in triplicate.

3.6. Tanning Effluent Treatment and Bio-Adsorption of Chromium Ions

The potential of MgO-NPs to decolorize the tanning effluent was investigated. Briefly, the tanning effluent was mixed with MgO-NPs (0.25, 0.5, 0.75, and 1.0 µg mL–1) for different contact times (30, 60, 90, 120, 150, 180, and 240 min) in a 250 mL conical flask under shaking conditions (150 rpm). Each treatment was performed in triplicate. The formed mixture was stirred for 30 min before the experiment reached absorption/desorption equilibrium. The decolorization ratio was measured at the end of each different contact time as follows.
Approximately 1.0 mL of the mixture (tanning effluent with MgO-NPs) was withdrawn, centrifuged at 5000 rpm for 8 min, and used to detect the optical density of the treated tanning effluent at the maximum λmax = 550 nm by a spectrophotometer (721 spectrophotometers, M-ETCAL). The decolorization ratio (%) of the tanning effluent was measured using the following equation [48].
D ( % ) = C 0 − C t C 0 × 100
where, D is the decolorization ratio %; C0 is the absorbance at zero time; Ct is the absorbance after specific time t (min).
At the optimum contact time and suitable MgO-NP concentration, the chemical parameters including biological oxygen demand (BOD), chemical oxygen demand (COD), total dissolved solids (TDS), total suspended solids (TSS), and conductivity were calculated according to the standard recommended methods [95].
Chromium (Cr) ion was the main common heavy metal present in the tanning effluent. Therefore, the Cr ion concentration before and after treatment with optimum MgO-NP concentration and optimum contact time was measured using atomic adsorption spectroscopy (A PerkinElmer Analyst 800 atomic spectrometer).

3.7. Statistical Analysis

The means of three replications and standard error (±SE) were calculated for all the results obtained. Data were subjected to statistical analysis by the statistical package SPSS v17. The mean difference comparison between the treatments was analyzed by t-tests or analysis of variance (ANOVA) and subsequently by Tukey’s HSD test at p < 0.05.

4. Conclusions

In the current study, MgO-NPs were fabricated through the reduction of Mg (NO3)2·6H2O by metabolites secreted by A. terreus strain S1. The first indicator for successful MgO-NP synthesis was a color change from colorless to turbid white and detection of maximum surface plasmon resonance at 280 nm. The various parameters such as metal precursor concentration, contact time, temperature, and pH values that affect the production process were optimized. The physicochemical characterization was achieved by TEM, SEM-EDX, XRD, DLS, and FT-IR spectroscopy. The role of fungal metabolites in the reduction, capping, and the stabilizing process was detected by FT-IR. Moreover, the MgO-NP size (8.0 to 38.0 nm), crystallographic structure, qualitative and quantitative compositions, and dispersion of NPs in colloid solution were confirmed by TEM, XRD, SEM-EDX, and DLS analyses, respectively. The antimicrobial activity of biosynthesized MgO-NPs was assessed against pathogenic S. aureus, B. subtilis, P. aeruginosa, E. coli, and C. albicans. Data showed that the inhibitory action of MgO-NPs was concentration-dependent. Further, the MIC value was detected as 50 μg mL–1 for P. aeruginosa with ZOI of 8.3 ± 0.3 mm, whereas E. coli, C. albicans, S. aureus, and B. subtilis had an MIC value 100 μg mL–1 with ZOIs of 8.0 ± 0.0, 8.7 ± 0.9, 8.0 ± 0.0, and 9.3 ± 0.6 mm, respectively. Moreover, biogenically synthesized MgO-NPs exhibited the ability to decolorize the greenish-blue color of tanning effluent with a percentage of 96.8 ± 1.7% after 150 min. At these decolorization percentages, the physicochemical parameters of tanning effluent including TSS, TDS, BOD, COD, and conductivity were highly reduced. Finally, the MgO-NPs showed high removal of chromium ions with a percentage of 97.5%. This study provides a promising eco-friendly, cost-effective, and biocompatible nanomaterial for various applications.

Author Contributions

Conceptualization, S.E.-D.H. and A.F.; methodology, E.S.; A.M.E.; S.E.-D.H.; S.S.S.; A.A.R.; M.H.; A.F.; software, E.S.; S.E.-D.H.; A.F.; validation, E.S.; A.M.E.; S.E.-D.H.; S.S.S.; A.A.R.; A.F.; formal analysis, E.S.; A.M.E.; S.E.-D.H.; S.S.S.; A.A.R.; M.H.; A.F.; investigation, E.S.; A.M.E.; S.E.-D.H.; S.S.S.; A.A.R.; M.H.; A.F.; resources, E.S.; A.M.E.; S.E.-D.H.; S.S.S.; A.A.R.; A.F. data curation, E.S.; A.M.E.; S.E.-D.H.; S.S.S.; A.A.R.; M.H.; A.F. writing—original draft preparation, E.S.; A.M.E.; A.A.R.; A.F. writing—review and editing, E.S.; A.M.E.; S.E.-D.H.; S.S.S.; A.A.R.; M.H.; A.F.; H.A.S.; E.M.S.; F.M.S. visualization, E.S.; A.M.E.; S.E.-D.H.; A.F.; supervision, E.S., S.E.-D.H.; A.F.; project administration, E.S., S.E.-D.H.; A.F.; funding acquisition, F.M.S., E.M.S. and H.A.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Acknowledgments

We appreciate and thank Taif University for the financial support for Taif University Researchers Supporting Project (TURSP-2020/07), Taif University, Taif, Saudi Arabia.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Song, M.; Wang, R.; Zeng, X. Water resources utilization efficiency and influence factors under environmental restrictions. J. Clean. Prod. 2018, 184, 611–621. [Google Scholar] [CrossRef]
  2. Jobby, R.; Jha, P.; Yadav, A.K.; Desai, N. Biosorption and biotransformation of hexavalent chromium [Cr(VI)]: A comprehensive review. Chemosphere 2018, 207, 255–266. [Google Scholar] [CrossRef] [PubMed]
  3. Selim, M.T.; Salem, S.S.; Mohamed, A.A.; El-Gamal, M.S.; Awad, M.F.; Fouda, A. Biological Treatment of Real Textile Effluent Using Aspergillus flavus and Fusarium oxysporium and Their Consortium along with the Evaluation of Their Phytotoxicity. J. Fungi 2021, 7, 193. [Google Scholar] [CrossRef] [PubMed]
  4. Hamza, M.F.; Hamad, N.A.; Hamad, D.M.; Khalafalla, M.S.; Abdel-Rahman, A.A.; Zeid, I.F.; Wei, Y.; Hessien, M.M.; Fouda, A.; Salem, W.M. Synthesis of Eco-Friendly Biopolymer, Alginate-Chitosan Composite to Adsorb the Heavy Metals, Cd(II) and Pb(II) from Contaminated Effluents. Materials 2021, 14, 2189. [Google Scholar] [CrossRef]
  5. Salem, S.S.; Mohamed, A.; El-Gamal, M.; Talat, M.; Fouda, A. Biological Decolorization and Degradation of Azo Dyes from Textile Wastewater Effluent by Aspergillus niger. Egypt. J. Chem. 2019, 62, 1799–1813. [Google Scholar]
  6. Ali, A.; Shaikh, I.A.; Abbasi, N.A.; Firdous, N.; Ashraf, M.N. Enhancing water efficiency and wastewater treatment using sustainable technologies: A laboratory and pilot study for adhesive and leather chemicals production. J. Water Process Eng. 2020, 36, 101308. [Google Scholar] [CrossRef]
  7. Wang, D.; He, S.; Shan, C.; Ye, Y.; Ma, H.; Zhang, X.; Zhang, W.; Pan, B. Chromium speciation in tannery effluent after alkaline precipitation: Isolation and characterization. J. Hazard. Mater. 2016, 316, 169–177. [Google Scholar] [CrossRef]
  8. Bhattacharya, A.; Gupta, A. Evaluation of Acinetobacter sp. B9 for Cr (VI) resistance and detoxification with potential application in bioremediation of heavy-metals-rich industrial wastewater. Environ. Sci. Pollut. Res. Int. 2013, 20, 6628–6637. [Google Scholar] [CrossRef]
  9. Soliman, A.M.; Abdel-Latif, W.; Shehata, I.H.; Fouda, A.; Abdo, A.M.; Ahmed, Y.M. Green Approach to Overcome the Resistance Pattern of Candida spp. Using Biosynthesized Silver Nanoparticles Fabricated by Penicillium chrysogenum F9. Biol. Trace Elem. Res. 2021, 199, 800–811. [Google Scholar] [CrossRef]
  10. Hamza, M.F.; Fouda, A.; Elwakeel, K.Z.; Wei, Y.; Guibal, E.; Hamad, N.A. Phosphorylation of Guar Gum/Magnetite/Chitosan Nanocomposites for Uranium (VI) Sorption and Antibacterial Applications. Molecules 2021, 26, 1920. [Google Scholar] [CrossRef]
  11. Salem, S.; Fouda, A. Green Synthesis of Metallic Nanoparticles and Their Prospective Biotechnological Applications: An Overview. Biol. Trace Elem. Res. 2020, 199, 344–370. [Google Scholar] [CrossRef]
  12. Badawy, A.A.; Abdelfattah, N.A.H.; Salem, S.S.; Awad, M.F.; Fouda, A. Efficacy Assessment of Biosynthesized Copper Oxide Nanoparticles (CuO-NPs) on Stored Grain Insects and Their Impacts on Morphological and Physiological Traits of Wheat (Triticum aestivum L.) Plant. Biology 2021, 10, 233. [Google Scholar] [CrossRef]
  13. Abinaya, S.; Kavitha, H.P.; Prakash, M.; Muthukrishnaraj, A. Green synthesis of magnesium oxide nanoparticles and its applications: A review. Sustain. Chem. Pharm. 2021, 19, 100368. [Google Scholar] [CrossRef]
  14. Vergheese, M.; Vishal, S.K. Green synthesis of magnesium oxide nanoparticles using Trigonella foenum-graecum leaf extract and its antibacterial activity. J. Pharm. Phytochem. 2018, 7, 1193–1200. [Google Scholar]
  15. Abdulkhaleq, N.A.; Nayef, U.M.; Albarazanchi, A.K.H. MgO nanoparticles synthesis via laser ablation stationed on porous silicon for photoconversion application. Optik 2020, 212, 164793. [Google Scholar] [CrossRef]
  16. Sofi, A.H.; Akhoon, S.A.; Mir, J.F.; Rather, M.U.D. Magnesium Oxide (MgO): A Viable Agent for Antimicrobial Activity. In Applications of Nanomaterials in Agriculture, Food Science, and Medicine; IGI Global: Hershey, PA, USA, 2021; pp. 98–105. [Google Scholar]
  17. Fouda, A.; Awad, M.A.; Eid, A.M.; Saied, E.; Barghoth, M.G.; Hamza, M.F.; Awad, M.F.; Abdelbary, S.; Hassan, S.E. An Eco-Friendly Approach to the Control of Pathogenic Microbes and Anopheles stephensi Malarial Vector Using Magnesium Oxide Nanoparticles (Mg-NPs) Fabricated by Penicillium chrysogenum. Int. J. Mol. Sci. 2021, 22, 5096. [Google Scholar] [CrossRef]
  18. Refat, M.S.; Ibrahim, H.K.; Sowellim, S.Z.A.; Soliman, M.H.; Saeed, E.M. Spectroscopic and Thermal Studies of Mn(II), Fe(III), Cr(III) and Zn(II) Complexes Derived from the Ligand Resulted by the Reaction Between 4-Acetyl Pyridine and Thiosemicarbazide. J. Inorg. Organomet. Polym. 2009, 19, 521. [Google Scholar] [CrossRef]
  19. Jagadeeshan, S.; Parsanathan, R. Nano-metal oxides for antibacterial activity. In Advanced Nanostructured Materials for Environmental Remediation; Springer: Cham, Switzerland, 2019; pp. 59–90. [Google Scholar]
  20. Srivastava, V.; Sharma, Y.C.; Sillanpää, M. Green synthesis of magnesium oxide nanoflower and its application for the removal of divalent metallic species from synthetic wastewater. Ceram. Int. 2015, 41, 6702–6709. [Google Scholar] [CrossRef]
  21. Parham, S.; Wicaksono, D.H.B.; Bagherbaigi, S.; Lee, S.L.; Nur, H. Antimicrobial Treatment of Different Metal Oxide Nanoparticles: A Critical Review. J. Chin. Chem. Soc. 2016, 63, 385–393. [Google Scholar] [CrossRef]
  22. Saravanathamizhan, R.; Perarasu, V.T. Chapter 6—Improvement of Biodegradability Index of Industrial Wastewater Using Different Pretreatment Techniques. In Wastewater Treatment; Shah, M.P., Sarkar, A., Mandal, S., Eds.; Elsevier: Amsterdam, The Netherlands, 2021; pp. 103–136. [Google Scholar]
  23. Rani, P.; Kaur, G.; Rao, K.V.; Singh, J.; Rawat, M. Impact of Green Synthesized Metal Oxide Nanoparticles on Seed Germination and Seedling Growth of Vigna radiata (Mung Bean) and Cajanus cajan (Red Gram). J. Inorg. Organomet. Polym. Mater. 2020, 30, 4053–4062. [Google Scholar] [CrossRef]
  24. Eid, A.M.; Fouda, A.; Niedbała, G.; Hassan, S.E.-D.; Salem, S.S.; Abdo, A.M.; Hetta, H.F.; Shaheen, T.I. Endophytic Streptomyces laurentii Mediated Green Synthesis of Ag-NPs with Antibacterial and Anticancer Properties for Developing Functional Textile Fabric Properties. Antibiotics 2020, 9, 641. [Google Scholar] [CrossRef] [PubMed]
  25. Samak, D.H.; El-Sayed, Y.S.; Shaheen, H.M.; El-Far, A.H.; Abd El-Hack, M.E.; Noreldin, A.E.; El-Naggar, K.; Abdelnour, S.A.; Saied, E.M.; El-Seedi, H.R.; et al. Developmental Toxicity of Carbon Nanoparticles during Embryogenesis in Chicken. Environ Sci Pollut Res 2020, 27, 19058–19072. [Google Scholar] [CrossRef] [PubMed]
  26. McClenny, N. Laboratory detection and identification of Aspergillus species by microscopic observation and culture: The traditional approach. Med. Mycol. 2005, 43 (Suppl. 1), S125–S128. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  27. Diba, K.; Kordbacheh, P.; Mirhendi, S.; Rezaie, S.; Mahmoudi, M. Identification of Aspergillus species using morphological characteristics. Pak. J. Med Sci. 2007, 23, 867. [Google Scholar]
  28. Risslegger, B.; Zoran, T.; Lackner, M.; Aigner, M.; Sánchez-Reus, F.; Rezusta, A.; Chowdhary, A.; Taj-Aldeen, S.J.; Arendrup, M.C.; Oliveri, S.; et al. A prospective international Aspergillus terreus survey: An EFISG, ISHAM and ECMM joint study. Clin. Microbiol. Infect. Off. Publ. Eur. Soc. Clin. Microbiol. Infect. Dis. 2017, 23, 776.e1–776.e5. [Google Scholar] [CrossRef] [Green Version]
  29. Subhan, M.; Faryal, R.; Macreadie, I. Exploitation of Aspergillus terreus for the Production of Natural Statins. J. Fungi 2016, 2, 13. [Google Scholar] [CrossRef]
  30. Sethi, B.K.; Nanda, P.K.; Sahoo, S. Characterization of biotechnologically relevant extracellular lipase produced by Aspergillus terreus NCFT 4269.10. Braz. J. Microbiol. 2016, 47, 143–149. [Google Scholar] [CrossRef] [Green Version]
  31. Raliya, R.; Tarafdar, J.C. Biosynthesis and characterization of zinc, magnesium and titanium nanoparticles: An eco-friendly approach. Int. Nano Lett. 2014, 4, 93. [Google Scholar] [CrossRef] [Green Version]
  32. Lashin, I.; Fouda, A.; Gobouri, A.A.; Azab, E.; Mohammedsaleh, Z.M.; Makharita, R.R. Antimicrobial and In Vitro Cytotoxic Efficacy of Biogenic Silver Nanoparticles (Ag-NPs) Fabricated by Callus Extract of Solanum incanum L. Biomolecules 2021, 11, 341. [Google Scholar] [CrossRef]
  33. Grijseels, S.; Nielsen, J.C.; Nielsen, J.; Larsen, T.O.; Frisvad, J.C.; Nielsen, K.F.; Frandsen, R.J.N.; Workman, M. Physiological characterization of secondary metabolite producing Penicillium cell factories. Fungal Biol. Biotechnol. 2017, 4, 8. [Google Scholar] [CrossRef] [Green Version]
  34. Shaheen, T.I.; Fouda, A.; Salem, S.S. Integration of Cotton Fabrics with Biosynthesized CuO Nanoparticles for Bactericidal Activity in the Terms of Their Cytotoxicity Assessment. Ind. Eng. Chem. Res. 2021, 60, 1553–1563. [Google Scholar] [CrossRef]
  35. Hassan, S.E.-D.; Fouda, A.; Radwan, A.A.; Salem, S.S.; Barghoth, M.G.; Awad, M.A.; Abdo, A.M.; El-Gamal, M.S. Endophytic actinomycetes Streptomyces spp mediated biosynthesis of copper oxide nanoparticles as a promising tool for biotechnological applications. JBIC J. Biol. Inorg. Chem. 2019, 24, 377–393. [Google Scholar] [CrossRef]
  36. Loo, Y.Y.; Rukayadi, Y.; Nor-Khaizura, M.-A.-R.; Kuan, C.H.; Chieng, B.W.; Nishibuchi, M.; Radu, S. In Vitro Antimicrobial Activity of Green Synthesized Silver Nanoparticles Against Selected Gram-negative Foodborne Pathogens. Front. Microbiol. 2018, 9, 1555. [Google Scholar] [CrossRef]
  37. Nguyen, D.T.C.; Dang, H.H.; Vo, D.-V.N.; Bach, L.G.; Nguyen, T.D.; Tran, T.V. Biogenic synthesis of MgO nanoparticles from different extracts (flower, bark, leaf) of Tecoma stans (L.) and their utilization in selected organic dyes treatment. J. Hazard. Mater. 2021, 404, 124146. [Google Scholar] [CrossRef]
  38. Ogunyemi, S.O.; Zhang, F.; Abdallah, Y.; Zhang, M.; Wang, Y.; Sun, G.; Qiu, W.; Li, B. Biosynthesis and characterization of magnesium oxide and manganese dioxide nanoparticles using Matricaria chamomilla L. extract and its inhibitory effect on Acidovorax oryzae strain RS-2. Artif. Cells Nanomed. Biotechnol. 2019, 47, 2230–2239. [Google Scholar] [CrossRef] [Green Version]
  39. Hamida, R.S.; Ali, M.A.; Abdelmeguid, N.E.; Al-Zaban, M.I.; Baz, L.; Bin-Meferij, M.M. Lichens—A Potential Source for Nanoparticles Fabrication: A Review on Nanoparticles Biosynthesis and Their Prospective Applications. J. Fungi 2021, 7, 291. [Google Scholar] [CrossRef]
  40. Mohd Yusof, H.; Mohamad, R.; Zaidan, U.H.; Abdul Rahman, N.A. Microbial synthesis of zinc oxide nanoparticles and their potential application as an antimicrobial agent and a feed supplement in animal industry: A review. J. Anim. Sci. Biotechnol. 2019, 10, 57. [Google Scholar] [CrossRef]
  41. Hassan, S.E.; Fouda, A.; Saied, E.; Farag, M.M.S.; Eid, A.M.; Barghoth, M.G.; Awad, M.A.; Hamza, M.F.; Awad, M.F. Rhizopus oryzae-Mediated Green Synthesis of Magnesium Oxide Nanoparticles (MgO-NPs): A Promising Tool for Antimicrobial, Mosquitocidal Action, and Tanning Effluent Treatment. J. Fungi 2021, 7, 372. [Google Scholar] [CrossRef]
  42. Muangban, J.; Jaroenapibal, P. Effects of precursor concentration on crystalline morphologies and particle sizes of electrospun WO3 nanofibers. Ceram. Int. 2014, 40, 6759–6764. [Google Scholar] [CrossRef]
  43. Jeevanandam, J.; San Chan, Y.; Jing Wong, Y.; Siang Hii, Y. Biogenic synthesis of magnesium oxide nanoparticles using Aloe barbadensis leaf latex extract. IOP Conf. Ser. Mater. Sci. Eng. 2020, 943, 012030. [Google Scholar] [CrossRef]
  44. Naseem, K.; Zia Ur Rehman, M.; Ahmad, A.; Dubal, D.; AlGarni, T.S. Plant Extract Induced Biogenic Preparation of Silver Nanoparticles and Their Potential as Catalyst for Degradation of Toxic Dyes. Coatings 2020, 10, 1235. [Google Scholar] [CrossRef]
  45. Irfan, M.; Moniruzzaman, M.; Ahmad, T.; Samsudin, M.F.R.; Bashir, F.; Butt, M.T.; Ashraf, H. Identifying the role of process conditions for synthesis of stable gold nanoparticles and insight detail of reaction mechanism. Inorg. Nano Met. Chem. 2021, 1–14. [Google Scholar] [CrossRef]
  46. Sahu, P.K.; Sahu, P.K.; Agarwal, D.D. Role of basicity and the catalytic activity of KOH loaded MgO and hydrotalcite as catalysts for the efficient synthesis of 1-[(2-benzothiazolylamino)arylmethyl]-2-naphthalenols. RSC Adv. 2015, 5, 69143–69151. [Google Scholar] [CrossRef]
  47. Vijayanandan, A.S.; Balakrishnan, R.M. Biosynthesis of cobalt oxide nanoparticles using endophytic fungus Aspergillus nidulans. J. Environ. Manag. 2018, 218, 442–450. [Google Scholar] [CrossRef]
  48. Fouda, A.; Hassan, S.E.-D.; Abdel-Rahman, M.A.; Farag, M.M.S.; Shehal-deen, A.; Mohamed, A.A.; Alsharif, S.M.; Saied, E.; Moghanim, S.A.; Azab, M.S. Catalytic degradation of wastewater from the textile and tannery industries by green synthesized hematite (α-Fe2O3) and magnesium oxide (MgO) nanoparticles. Curr. Res. Biotechnol. 2021, 3, 29–41. [Google Scholar] [CrossRef]
  49. Ahmadi, M.; Ghasemi, M.R.; Rafsanjani, H.H. Study of different parameters in TiO2 nanoparticles formation. J. Mater. Sci. Eng. 2011, 5, 87. [Google Scholar]
  50. Fouda, A.; Abdel-Maksoud, G.; Saad, H.A.; Gobouri, A.A.; Mohammedsaleh, Z.M.; El-Sadany, M.A. The efficacy of silver nitrate (AgNO3) as a coating agentto protect paper against high deteriorating microbes. Catalysts 2021, 11, 310. [Google Scholar] [CrossRef]
  51. Amina, M.; Al Musayeib, N.M.; Alarfaj, N.A.; El-Tohamy, M.F.; Oraby, H.F.; Al Hamoud, G.A.; Bukhari, S.I.; Moubayed, N.M.S. Biogenic green synthesis of MgO nanoparticles using Saussurea costus biomasses for a comprehensive detection of their antimicrobial, cytotoxicity against MCF-7 breast cancer cells and photocatalysis potentials. PLoS ONE 2020, 15, e0237567. [Google Scholar] [CrossRef] [PubMed]
  52. Asami, H.; Tokugawa, M.; Masaki, Y.; Ishiuchi, S.-i.; Gloaguen, E.; Seio, K.; Saigusa, H.; Fujii, M.; Sekine, M.; Mons, M. Effective Strategy for Conformer-Selective Detection of Short-Lived Excited State Species: Application to the IR Spectroscopy of the N1H Keto Tautomer of Guanine. J. Phys. Chem. A 2016, 120, 2179–2184. [Google Scholar] [CrossRef] [PubMed]
  53. Dobrucka, R. Synthesis of MgO Nanoparticles Using Artemisia abrotanum Herba Extract and Their Antioxidant and Photocatalytic Properties. Iran. J. Sci. Technol. Trans. A Sci. 2018, 42, 547–555. [Google Scholar] [CrossRef] [Green Version]
  54. Brotton, S.J.; Lucas, M.; Jensen, T.N.; Anderson, S.L.; Kaiser, R.I. Spectroscopic Study on the Intermediates and Reaction Rates in the Oxidation of Levitated Droplets of Energetic Ionic Liquids by Nitrogen Dioxide. J. Phys. Chem. A 2018, 122, 7351–7377. [Google Scholar] [CrossRef]
  55. Karimi, B.; Khorasani, M.; Vali, H.; Vargas, C.; Luque, R. Palladium Nanoparticles Supported in the Nanospaces of Imidazolium-Based Bifunctional PMOs: The Role of Plugs in Selectivity Changeover in Aerobic Oxidation of Alcohols. ACS Catal. 2015, 5, 4189–4200. [Google Scholar] [CrossRef]
  56. Suresh, J.; Pradheesh, G.; Alexramani, V.; Sundrarajan, M.; Hong, S.I. Green synthesis and characterization of hexagonal shaped MgO nanoparticles using insulin plant (Costus pictus D. Don) leave extract and its antimicrobial as well as anticancer activity. Adv. Powder Technol. 2018, 29, 1685–1694. [Google Scholar] [CrossRef]
  57. Umaralikhan, L.; Jamal Mohamed Jaffar, M. Green Synthesis of MgO Nanoparticles and it Antibacterial Activity. Iran. J. Sci. Technol. Trans. A Sci. 2018, 42, 477–485. [Google Scholar] [CrossRef]
  58. Fouda, A.; Abdel-Maksoud, G.; Abdel-Rahman, M.A.; Eid, A.M.; Barghoth, M.G.; El-Sadany, M.A.-H. Monitoring the effect of biosynthesized nanoparticles against biodeterioration of cellulose-based materials by Aspergillus niger. Cellulose 2019, 26, 6583–6597. [Google Scholar] [CrossRef]
  59. Aref, M.S.; Salem, S.S. Bio-callus synthesis of silver nanoparticles, characterization, and antibacterial activities via Cinnamomum camphora callus culture. Biocatal. Agric. Biotechnol. 2020, 27, 101689. [Google Scholar] [CrossRef]
  60. Huang, L.; Li, D.; Lin, Y.; Evans, D.G.; Duan, X. Influence of nano-MgO particle size on bactericidal action againstBacillus subtilis var. niger. Chin. Sci. Bull. 2005, 50, 514–519. [Google Scholar] [CrossRef]
  61. Jian, W.; Ma, Y.; Wu, H.; Zhu, X.; Wang, J.; Xiong, H.; Lin, L.; Wu, L. Fabrication of highly stable silver nanoparticles using polysaccharide-protein complexes from abalone viscera and antibacterial activity evaluation. Int. J. Biol. Macromol. 2019, 128, 839–847. [Google Scholar] [CrossRef]
  62. Abdallah, Y.; Ogunyemi, S.O.; Abdelazez, A.; Zhang, M.; Hong, X.; Ibrahim, E.; Hossain, A.; Fouad, H.; Li, B.; Chen, J. The Green Synthesis of MgO Nano-Flowers Using Rosmarinus officinalis L. (Rosemary) and the Antibacterial Activities against Xanthomonas oryzae pv. oryzae. BioMed Res. Int. 2019, 2019, 5620989. [Google Scholar] [CrossRef] [Green Version]
  63. Jhansi, K.; Jayarambabu, N.; Reddy, K.P.; Reddy, N.M.; Suvarna, R.P.; Rao, K.V.; Kumar, V.R.; Rajendar, V. Biosynthesis of MgO nanoparticles using mushroom extract: Effect on peanut (Arachis hypogaea L.) seed germination. 3 Biotech 2017, 7, 263. [Google Scholar] [CrossRef]
  64. Alsharif, S.M.; Salem, S.S.; Abdel-Rahman, M.A.; Fouda, A.; Eid, A.M.; El-Din Hassan, S.; Awad, M.A.; Mohamed, A.A. Multifunctional properties of spherical silver nanoparticles fabricated by different microbial taxa. Heliyon 2020, 6, e03943. [Google Scholar] [CrossRef]
  65. Salem, S.S.; El-Belely, E.F.; Niedbała, G.; Alnoman, M.M.; Hassan, S.E.; Eid, A.M.; Shaheen, T.I.; Elkelish, A.; Fouda, A. Bactericidal and In-Vitro Cytotoxic Efficacy of Silver Nanoparticles (Ag-NPs) Fabricated by Endophytic Actinomycetes and Their Use as Coating for the Textile Fabrics. Nanomaterials 2020, 10, 2082. [Google Scholar] [CrossRef]
  66. Fouda, A.; Hassan, S.E.; Abdo, A.M.; El-Gamal, M.S. Antimicrobial, Antioxidant and Larvicidal Activities of Spherical Silver Nanoparticles Synthesized by Endophytic Streptomyces spp. Biol. Trace Elem. Res. 2020, 195, 707–724. [Google Scholar] [CrossRef]
  67. Fouda, A.; Hassan, S.E.-D.; Saied, E.; Azab, M.S. An eco-friendly approach to textile and tannery wastewater treatment using maghemite nanoparticles (γ-Fe2O3-NPs) fabricated by Penicillium expansum strain (K-w). J. Environ. Chem. Eng. 2021, 9, 104693. [Google Scholar] [CrossRef]
  68. Al-Hazmi, F.; Alnowaiser, F.; Al-Ghamdi, A.A.; Al-Ghamdi, A.A.; Aly, M.M.; Al-Tuwirqi, R.M.; El-Tantawy, F. A new large-scale synthesis of magnesium oxide nanowires: Structural and antibacterial properties. Superlattices Microstruct. 2012, 52, 200–209. [Google Scholar] [CrossRef] [Green Version]
  69. Karthik, K.; Dhanuskodi, S.; Gobinath, C.; Prabukumar, S.; Sivaramakrishnan, S. Fabrication of MgO nanostructures and its efficient photocatalytic, antibacterial and anticancer performance. J. Photochem. Photobiol. B Biol. 2019, 190, 8–20. [Google Scholar] [CrossRef] [PubMed]
  70. Wang, L.; Hu, C.; Shao, L. The antimicrobial activity of nanoparticles: Present situation and prospects for the future. Int. J. Nanomed. 2017, 12, 1227–1249. [Google Scholar] [CrossRef] [Green Version]
  71. Shaikh, S.; Nazam, N.; Rizvi, S.M.D.; Ahmad, K.; Baig, M.H.; Lee, E.J.; Choi, I. Mechanistic Insights into the Antimicrobial Actions of Metallic Nanoparticles and Their Implications for Multidrug Resistance. Int. J. Mol. Sci. 2019, 20, 2468. [Google Scholar] [CrossRef] [Green Version]
  72. Chiddarwar, S. Novel Approaches of Magnesium Oxide Nanoparticles in MIC, MBC, Antibiofilm and Antimicrobial Activities against Bacteria, Yeast and Biofilms. In Proceedings of the MBC, Antibiofilm and Antimicrobial Activities against Bacteria, Yeast and Biofilms, Hyderabad, India, 19 February 2020. [Google Scholar]
  73. Wong, C.W.; Chan, Y.S.; Jeevanandam, J.; Pal, K.; Bechelany, M.; Abd Elkodous, M.; El-Sayyad, G.S. Response Surface Methodology Optimization of Mono-dispersed MgO Nanoparticles Fabricated by Ultrasonic-Assisted Sol–Gel Method for Outstanding Antimicrobial and Antibiofilm Activities. J. Clust. Sci. 2020, 31, 367–389. [Google Scholar] [CrossRef]
  74. Fouda, A.; Salem, S.S.; Wassel, A.R.; Hamza, M.F.; Shaheen, T.I. Optimization of green biosynthesized visible light active CuO/ZnO nano-photocatalysts for the degradation of organic methylene blue dye. Heliyon 2020, 6, e04896. [Google Scholar] [CrossRef]
  75. Ye, W.; Liu, H.; Lin, F.; Lin, J.; Zhao, S.; Yang, S.; Hou, J.; Zhou, S.; van der Bruggen, B. High-flux nanofiltration membranes tailored by bio-inspired co-deposition of hydrophilic g-C3N4 nanosheets for enhanced selectivity towards organics and salts. Environ. Sci. Nano 2019, 6, 2958–2967. [Google Scholar] [CrossRef]
  76. Fouda, A.; Hassan, S.E.-D.; Saied, E.; Hamza, M.F. Photocatalytic degradation of real textile and tannery effluent using biosynthesized magnesium oxide nanoparticles (MgO-NPs), heavy metal adsorption, phytotoxicity, and antimicrobial activity. J. Environ. Chem. Eng. 2021, 9, 105346. [Google Scholar] [CrossRef]
  77. Kishor, R.; Purchase, D.; Saratale, G.D.; Saratale, R.G.; Ferreira, L.F.R.; Bilal, M.; Chandra, R.; Bharagava, R.N. Ecotoxicological and health concerns of persistent coloring pollutants of textile industry wastewater and treatment approaches for environmental safety. J. Environ. Chem. Eng. 2021, 9, 105012. [Google Scholar] [CrossRef]
  78. Li, S. Combustion synthesis of porous MgO and its adsorption properties. Int. J. Ind. Chem. 2019, 10, 89–96. [Google Scholar] [CrossRef] [Green Version]
  79. Ilyas, M.; Ahmad, W.; Khan, H.; Yousaf, S.; Yasir, M.; Khan, A. Environmental and health impacts of industrial wastewater effluents in Pakistan: A review. Rev. Environ. Health 2019, 34, 171–186. [Google Scholar] [CrossRef]
  80. Laxmi, V.; Kaushik, G. Toxicity of hexavalent chromium in environment, health threats, and its bioremediation and detoxification from tannery wastewater for environmental safety. In Bioremediation of Industrial Waste for Environmental Safety; Springer: Singapore, 2020; pp. 223–243. [Google Scholar]
  81. Sawalha, H.; Alsharabaty, R.; Sarsour, S.; Al-Jabari, M. Wastewater from leather tanning and processing in Palestine: Characterization and management aspects. J. Environ. Manag. 2019, 251, 109596. [Google Scholar] [CrossRef]
  82. Barnhart, J. Occurrences, uses, and properties of chromium. Regul. Toxicol. Pharmacol. RTP 1997, 26, S3–S7. [Google Scholar] [CrossRef]
  83. Mohanty, K.; Jha, M.; Meikap, B.C.; Biswas, M.N. Removal of chromium (VI) from dilute aqueous solutions by activated carbon developed from Terminalia arjuna nuts activated with zinc chloride. Chem. Eng. Sci. 2005, 60, 3049–3059. [Google Scholar] [CrossRef]
  84. Mahdavi, S.; Jalali, M.; Afkhami, A. Heavy metals removal from aqueous solutions using TiO2, MgO, and Al2O3 nanoparticles. Chem. Eng. Commun. 2013, 200, 448–470. [Google Scholar] [CrossRef]
  85. Gusain, R.; Gupta, K.; Joshi, P.; Khatri, O.P. Adsorptive removal and photocatalytic degradation of organic pollutants using metal oxides and their composites: A comprehensive review. Adv. Colloid Interface Sci. 2019, 272, 102009. [Google Scholar] [CrossRef]
  86. Yang, J.; Hou, B.; Wang, J.; Tian, B.; Bi, J.; Wang, N.; Li, X.; Huang, X. Nanomaterials for the Removal of Heavy Metals from Wastewater. Nanomaterials 2019, 9, 424. [Google Scholar] [CrossRef] [Green Version]
  87. Jain, M.; Garg, V.K.; Kadirvelu, K. Equilibrium and kinetic studies for sequestration of Cr(VI) from simulated wastewater using sunflower waste biomass. J. Hazard. Mater. 2009, 171, 328–334. [Google Scholar] [CrossRef]
  88. Mohan, D.; Pittman, C.U., Jr. Activated carbons and low cost adsorbents for remediation of tri- and hexavalent chromium from water. J. Hazard. Mater. 2006, 137, 762–811. [Google Scholar] [CrossRef]
  89. Jain, M.; Yadav, M.; Kohout, T.; Lahtinen, M.; Garg, V.K.; Sillanpää, M. Development of iron oxide/activated carbon nanoparticle composite for the removal of Cr(VI), Cu(II) and Cd(II) ions from aqueous solution. Water Resour. Ind. 2018, 20, 54–74. [Google Scholar] [CrossRef]
  90. Hashem, A.H.; Saied, E.; Hasanin, M.S. Green and ecofriendly bio-removal of methylene blue dye from aqueous solution using biologically activated banana peel waste. Sustain. Chem. Pharm. 2020, 18, 100333. [Google Scholar] [CrossRef]
  91. Fouda, A.; Abdel-Maksoud, G.; Abdel-Rahman, M.A.; Salem, S.S.; Hassan, S.E.-D.; El-Sadany, M.A.-H. Eco-friendly approach utilizing green synthesized nanoparticles for paper conservation against microbes involved in biodeterioration of archaeological manuscript. Int. Biodeterior. Biodegrad. 2019, 142, 160–169. [Google Scholar] [CrossRef]
  92. Essien, E.R.; Atasie, V.N.; Okeafor, A.O.; Nwude, D.O. Biogenic synthesis of magnesium oxide nanoparticles using Manihot esculenta (Crantz) leaf extract. Int. Nano Lett. 2020, 10, 43–48. [Google Scholar] [CrossRef] [Green Version]
  93. Fouda, A.; El-Din Hassan, S.; Salem, S.S.; Shaheen, T.I. In-Vitro cytotoxicity, antibacterial, and UV protection properties of the biosynthesized Zinc oxide nanoparticles for medical textile applications. Microb. Pathog. 2018, 125, 252–261. [Google Scholar] [CrossRef]
  94. El-Belely, E.F.; Farag, M.M.S.; Said, H.A.; Amin, A.S.; Azab, E.; Gobouri, A.A.; Fouda, A. Green Synthesis of Zinc Oxide Nanoparticles (ZnO-NPs) Using Arthrospira platensis (Class: Cyanophyceae) and Evaluation of their Biomedical Activities. Nanomaterials 2021, 11, 95. [Google Scholar] [CrossRef]
  95. Oladipo, A.A.; Adeleye, O.J.; Oladipo, A.S.; Aleshinloye, A.O. Bio-derived MgO nanopowders for BOD and COD reduction from tannery wastewater. J. Water Process Eng. 2017, 16, 142–148. [Google Scholar] [CrossRef]
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Figure 1. Phylogenetic tree of the fungal strain S1 with the sequences from NCBI. The symbol ♦ refers to ITS fragments retrieved from this study. The tree was constructed with MEGA 6.1 using the neighbor-joining method.
Figure 1. Phylogenetic tree of the fungal strain S1 with the sequences from NCBI. The symbol ♦ refers to ITS fragments retrieved from this study. The tree was constructed with MEGA 6.1 using the neighbor-joining method.
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Figure 2. UV-Vis spectroscopy of myco-synthesized MgO-NPs showed maximum SPR at 280 nm.
Figure 2. UV-Vis spectroscopy of myco-synthesized MgO-NPs showed maximum SPR at 280 nm.
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Figure 3. Optimizing factors for biogenic MgO-NPs using A. terreus strain S1. (A) denotes the different Mg(NO3)2·6H2O concentrations; (B) denotes the contact time between biomass filtrate and optimum Mg(NO3)2·6H2O concentration; (C) illustrates the effect of pH values, and (D) denotes the effect of incubation temperature on biogenic MgO-NPs.
Figure 3. Optimizing factors for biogenic MgO-NPs using A. terreus strain S1. (A) denotes the different Mg(NO3)2·6H2O concentrations; (B) denotes the contact time between biomass filtrate and optimum Mg(NO3)2·6H2O concentration; (C) illustrates the effect of pH values, and (D) denotes the effect of incubation temperature on biogenic MgO-NPs.
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Figure 4. The FT-IR spectrum of myco-synthesized MgO-NPs fabricated by metabolites of A. terreus strain S1.
Figure 4. The FT-IR spectrum of myco-synthesized MgO-NPs fabricated by metabolites of A. terreus strain S1.
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Figure 5. Characterization of MgO-NPs synthesized by A. terreus strain S1, (A) TEM image; (B) size distribution according to the TEM image.
Figure 5. Characterization of MgO-NPs synthesized by A. terreus strain S1, (A) TEM image; (B) size distribution according to the TEM image.
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Figure 6. Characterization of MgO-NPs synthesized by A. terreus strain S1, (A) SEM image; (B) EDX profile.
Figure 6. Characterization of MgO-NPs synthesized by A. terreus strain S1, (A) SEM image; (B) EDX profile.
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Figure 7. (A) The XRD analysis of the crystallographic structure; (B) the DLS analysis of biogenically synthesized MgO-NPs.
Figure 7. (A) The XRD analysis of the crystallographic structure; (B) the DLS analysis of biogenically synthesized MgO-NPs.
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Figure 8. The antimicrobial activity of different concentrations of biogenically synthesized MgO-NPs against Staphylococcus aureus, Bacillus subtilis, Pseudomonas aeruginosa, and Escherichia coli, and Candida albicans. Different letters (a, b, c, and d) on bars at the same concertation refer that the mean values are significantly different (p ≤ 0.05) (n = 3).
Figure 8. The antimicrobial activity of different concentrations of biogenically synthesized MgO-NPs against Staphylococcus aureus, Bacillus subtilis, Pseudomonas aeruginosa, and Escherichia coli, and Candida albicans. Different letters (a, b, c, and d) on bars at the same concertation refer that the mean values are significantly different (p ≤ 0.05) (n = 3).
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Figure 9. The decolorization of tanning effluent using biogenically synthesized MgO-NPs by A. terreus strain S1.
Figure 9. The decolorization of tanning effluent using biogenically synthesized MgO-NPs by A. terreus strain S1.
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Table
Table 1. Decolorization percentages (%) of tanning effluent using different concentrations (0.25, 0.5, 0.75, and 1.0 µg mL−1) of myco-synthesized MgO-NPs at different contact times (30, 60, 90, 120, 150, 180, and 240 min).
Table 1. Decolorization percentages (%) of tanning effluent using different concentrations (0.25, 0.5, 0.75, and 1.0 µg mL−1) of myco-synthesized MgO-NPs at different contact times (30, 60, 90, 120, 150, 180, and 240 min).
MgO-NPs ConcentrationDecolorization Percentages (%) after the Time (min)
30 min60 min90 min120 min150 min180 min240 min
Control1.9 ± 0.22.2 ± 0.23.1 ± 0.33.8 ± 0.44.5 ± 0.35.2 ± 0.35.8 ± 0.4
0.25 µg mL–116.1 ± 1.618.4 ± 1.721.3 ± 2.126.5 ± 2.231.3 ± 2.238.5 ± 2.0546.6 ± 3.2
0.5 µg mL–128.5 ± 2.738.3 ± 2.245.7 ± 3.150.7 ± 3.754.8 ± 2.0159.4 ± 2.561.6 ± 1.8
0.75 µg mL–137.8 ± 2.249.3 ± 3.358.9 ± 2.669.7 ± 1.978.4 ± 1.781.4 ± 0.382.2 ± 1.7
1.0 µg mL–153.5 ± 3.667.4 ± 1.977.8 ± 1.389.1 ± 1.696.8 ± 1.797.5 ± 1.697.7 ± 1.7
Data are represented as the mean ± SD (n = 3).
Table
Table 2. Physicochemical characterization and chromium ion adsorption from tanning effluent by MgO-NPs.
Table 2. Physicochemical characterization and chromium ion adsorption from tanning effluent by MgO-NPs.
Physicochemical ParametersControlAfter MgO-NPs TreatmentRemoval Percentages (%)
pH10.58-
TSS (mg L–1)8776.3 ± 5.8 a172.0 ± 4.8 b98.04
TDS (mg L–1)15,720 ± 4.1 a252.0 ± 4.1 b98.3
BOD (mg L–1)2345.7 ± 7.0 a255.0 ± 5.1 b89.1
COD (mg L–1)641.7 ± 4.7 a18.0 ± 1.9 b97.2
Conductivity (S m–1)26,750.7 ± 6.0 a628.0 ± 3.8 b97.7
Cr mg L–1835.3 ± 2.5 a21.0 ± 0.7 b97.5
Different letters in the same row are significantly different (p ≤ 0.05) based on the Tukey LSD test. Data are presented as the mean ± SD (n = 3).
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Saied, E.; Eid, A.M.; Hassan, S.E.-D.; Salem, S.S.; Radwan, A.A.; Halawa, M.; Saleh, F.M.; Saad, H.A.; Saied, E.M.; Fouda, A. The Catalytic Activity of Biosynthesized Magnesium Oxide Nanoparticles (MgO-NPs) for Inhibiting the Growth of Pathogenic Microbes, Tanning Effluent Treatment, and Chromium Ion Removal. Catalysts 2021, 11, 821. https://doi.org/10.3390/catal11070821

AMA Style

Saied E, Eid AM, Hassan SE-D, Salem SS, Radwan AA, Halawa M, Saleh FM, Saad HA, Saied EM, Fouda A. The Catalytic Activity of Biosynthesized Magnesium Oxide Nanoparticles (MgO-NPs) for Inhibiting the Growth of Pathogenic Microbes, Tanning Effluent Treatment, and Chromium Ion Removal. Catalysts. 2021; 11(7):821. https://doi.org/10.3390/catal11070821

Chicago/Turabian Style

Saied, Ebrahim, Ahmed M. Eid, Saad El-Din Hassan, Salem S. Salem, Ahmed A. Radwan, Mahmoud Halawa, Fayez M. Saleh, Hosam A. Saad, Essa M. Saied, and Amr Fouda. 2021. "The Catalytic Activity of Biosynthesized Magnesium Oxide Nanoparticles (MgO-NPs) for Inhibiting the Growth of Pathogenic Microbes, Tanning Effluent Treatment, and Chromium Ion Removal" Catalysts 11, no. 7: 821. https://doi.org/10.3390/catal11070821

APA Style

Saied, E., Eid, A. M., Hassan, S. E.-D., Salem, S. S., Radwan, A. A., Halawa, M., Saleh, F. M., Saad, H. A., Saied, E. M., & Fouda, A. (2021). The Catalytic Activity of Biosynthesized Magnesium Oxide Nanoparticles (MgO-NPs) for Inhibiting the Growth of Pathogenic Microbes, Tanning Effluent Treatment, and Chromium Ion Removal. Catalysts, 11(7), 821. https://doi.org/10.3390/catal11070821

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