Applications of Nano Composites for Heavy Metal Removal from Water by Adsorption: Mini Review

Document Type : Research Paper

Authors

1 Department of Chemistry, College of Science, University of Al-Qadisiyah, Diwaniya 1753, Iraq

2 Department of Chemistry, College of Education, University of Al-Qadisiyah, Diwaniyah, Iraq

3 Department of Chemistry, The University of Lahore, Lahore, Pakistan

4 Department of Chemistry, University of Sahiwal, Sahiwal, Pakistan

5 Department of Chemistry, Government College University Faisalabad, Faisalabad, Pakistan

10.22052/JNS.2024.04.023

Abstract

The increasing contamination of water by various heavy metals has emerged as a pressing global issue, threatening human health, aquatic ecosystems, and agricultural sustainability. These heavy metals are required to remove through cost effective and efficient removal approaches due to their toxicity, persistence and bioaccumulation. This review explores the transformative potential of nanocomposites as advanced adsorbents for heavy metal elimination. By investigating their synthesis, characterization, and functional classifications, the study highlights how these materials outperform conventional methods through enhanced surface properties and adsorption efficiency. A comparative analysis of adsorption mechanisms, such as ion exchange, electrostatic interactions, and complexation, is addressed, alongside evaluations of critical operational parameters like pH, contact time, and percentage removal. Additionally, the paper also outlines the limitations of current nanocomposite technologies, such as scalability challenges and environmental concerns, while potential future options for the removal of heavy metals. This review sets the groundwork for future nanomaterials developed to address global water decontamination by extending knowledge in this field.    

Keywords


INTRODUCTION

One of the most essential needs for life is water. It is like lifeblood of our earth. It is silent hero, maintaining our universe from cellular processes to global ecosystem. Around 0.3% of the water resources in this world are drinkable[1]. Unfortunately, water pollution is now the most pressing global issue and it is urgent need to evaluate water management policy to tackle this problem[2]. Both developed and developing countries are facing this issue. Multiple organic and inorganic contaminants emitted from both natural and anthropogenic sources have caused the quality of water supplies to deteriorate drastically. When undesirable water bodies spread across a water system, the quality of the water changes, leading to water pollution[3-14]. There are many factors which can contribute to water pollution. Rapidly growing population, fast industrialization, expanding urbanization, and inappropriate use of natural resources have all had a detrimental impact on water quality in recent decades[15]. More than 1500 substances have been identified as contaminants[16]. Organic matter, nutrients, drugs. and cosmetics, poly- and perfluoroalkyl compounds, chemicals, heavy metals, dyes, radioactive materials, plastic items, nanoparticles, and pathogens are the contaminants of the primary concern[17, 18]. Among these contaminants, heavy metals are the most toxic pollutants due to their poisonous nature and chemical reactivity. These heavy metals (Zn, Pb, Cu, Cd, Cr, Ni, Hg, Ag etc.) enter into water supplies directly or indirectly[19]. These metals remain in the environment for longer time as they are non-biodegradable and have various oxidation states. Heavy metals have potential to cover long distances in the environment. Therefore, it is very important to eliminate all these pollutants especially heavy metals from wastewater before they are released into water supplies.

A number of techniques have been reported for waste water treatment, including adsorption membrane filtration, precipitation flocculation, Coagulation, electrolytic extraction, Fenton’s process, ion exchange, reverse osmosis, Constructed Wetlands, biological removal, and reduction[20-22]. These methodologies, however, have certain limitations and challenges associated with their applications in water treatment [23-28]. High cost, less efficiency, production of waste as by-product, low reliability, expensive equipment, and complex operating system are some drawbacks of these listed techniques. Besides these techniques, adsorption is one of the best and simple method used for the elimination of the heavy metals from water [4-11, 13, 14, 29-40]. The adsorption approach for removing contaminants has been found to be highly efficient, economical, and simple to use.

Various materials are employed for heavy metals removal from water. Nanoscale materials are widely used to treat water. These materials have unique properties because of their tiny size and high surface area to volume ratio. Due to these characteristics, nanocomposites exhibit high removal efficiency. Alongside their large surface area, nanocomposites show exceptional catalytic properties which make them suitable adsorbents for heavy metals removal from water. Their large surface area provides greater number of active sites for species to be removed. Therefore, they are the best materials for heavy metal decontamination.

The objectives of this review are to address an urgent need for effective and sustainable solutions for heavy metal contamination in water.  This includes exploring the latest advancements in the synthesis, structural characterization, and applications of nanocomposites for the adsorptive removal of heavy metals from aqueous solutions, evaluating the adsorption mechanisms, such as diffusion, electrostatic interactions, and redox reactions, Investigating the factors influencing adsorption performance, including pH, contact time, and surface modifications. Identifying the most efficient nanocomposite materials based on adsorption capacity, removal efficiency, and recyclibility to provide a comparative framework for material selection is main objective of this study. This review also discusses critical analysis of practical limitations of nanocomposite applications, such as high production costs, environmental concerns, and scalability, and suggesting possible solutions for overcoming these barriers.  This paper also proposes innovative strategies for developing eco-friendly and cost-effective nanocomposites that can work efficiently and align perfectly with the global standards.

This review distinguishes itself by offering a multidisciplinary approach on the use of novel and efficient nanocomposites for heavy metal removal, bridging gaps between material science, environmental engineering, and sustainable development. Unlike previous studies, this paper compares the adsorption efficiencies of nanocomposites extensively and relates them to their structural and functional properties. Additionally, it offers an extensive review of the adsorption mechanisms, explaining the role of complexation, surface contacts, and redox processes in high removal percentage. The paper also presents the idea of integrating nanocomposites into hybrid water treatment systems to optimize their potential. In order to ensure that future advancements in water purification technologies are in line with the Sustainable Development Goals of the UN, this study provides a bedrock for future developments by addressing economic and environmental challenges and suggesting directions for green synthesis and recyclability.

HEAVY METALS

Among all these toxic substances, heavy metals have the most adverse effect on environment because their concentration in water, soil and air is increasing tremendously as a result of anthropogenic activities. Any metal, irrespective of its density or atomic mass, that is hazardous is considered a heavy metal[41]. Some lighter elements such as aluminium, arsenic, selenium and metalloids are harmful for environment and considered as heavy metals while some heavy metals such as gold is non-toxic[42]. According to United States Environmental Protection Agency (USEPA), heavy metals can be arranged on the basis of maximum contaminant level (MCL) in following order[43]. Zinc (0.80) > Copper (0.25) > Nickel (0.20) > Chromium (0.05) > Arsenic (0.050) > Cadmium (0.01) > Lead (0.006) > Mercury (0.00003) 

Heavy metals can be classified into two main categories on the basis of their importance for plant and animal growth. Group 1 consists of elements such as B, Cu, Fe, Mo, Ni, and Zn which are considered vital for the plant and animal development. These metals become toxic when their concentration exceeds to a certain limit. Group 2 consists of As, Cd, Hg, and Pb which are not important for the animal and plants growth[44].

Rapid industrialization and urbanization along with extensive use of fertilizers and pesticides have posed serious threats to the environment due to increasing heavy metals concentration in our ecosystem[45]. Some of the primary sources of heavy metal pollution are Industries such as metal processing, electroplating, and chemical manufacturing often use and release heavy metals into the air, water, and soil, Improper disposal of electronic waste, batteries, auto-mobiles, and other metal-containing products can lead to heavy metal contamination of soil and water. Activities like leaching, dust emissions, wastewater discharge and natural activities such as Burning fossil fuels like coal and oil, volcanic eruption, metal corrosion, soil erosion, geological weathering release heavy metals into the atmosphere, which can then be deposited in soil and water bodies[46].

Industrial effluent containing heavy metals have high solubility in water and get mixed with water and soil which alters the composition of these natural medium[47]. These heavy metals are non-biodegradable in nature so they mix with water and soil and cause contamination of the food chain[48]. The pollution caused by these heavy metals are mostly long lasting, adverse and irreversible in nature. Prolonged intake of heavy metals may cause internal abnormalities as body begins to accumulate these toxic substances and use as required elements[49]. Arsenic, lead, mercury, and cadmium are the heavy metals that the World Health Organization (WHO) has included among the top 10 toxic substances because of their high toxicity and ecological resilience[50]. The biotoxicity of the heavy metals like zinc, copper, lead, arsenic, aluminium, and mercury are diarrhea, tremors, gastrointestinal disorders, vomiting, paralysis, depression, liver damage, insomnia, carcinogen, rheumatoid arthritis, stomatitis, renal disorder, depression, nausea, convulsion and pneumonia[51]. Apart from humans, animals and plants are also severely affected by these toxic heavy metals. High lead concentration in soil decreases soil efficiency while low lead concentration can cease biological mechanisms like transpiration, photosynthesis and mitosis which result in dark green color of the leaves and short roots[52].

 

NANOCOMPOSITE

Due to all these adverse effects of heavy metals, several materials are employed for the removal of the heavy metals. This review paper will focus on nanocomposites. The term “nano-composite material” developed over time to include a wide range of systems, including one, two, three, and amorphous materials, which are composed of specifically different components and assembled at the nanoscale[53]. Nanocomposites are the materials with nanoscale structure that enhance the macroscopic properties of the substance [54-56]. The nanocomposite material is a customized modern materials with the ability to remove fillers from a number of different substrates[54]. Nanocomposite are actually nanomaterials that integrate more than one distinct components to produce a composite, at least one dimension in nano range (1nm=10-9m), which has the finest characteristics of each component. Nanoparticles such as clay, metals, carbon nanotubes serve as filler in nanocomposites. Nanocomposite have advance properties and advantages[57]. 1) Only a small concentration of nano-filler is required to enhances their properties. 2) These materials are lighter in weight as compared to other composites. 3) Nanocomposites have improved properties that depends upon size such as thermal, chemical, mechanical, optical, magnetic and electrical properties.

          

Nanocomposite based purification

Conventional water treatment techniques such as coagulation-flocculation, reverse osmosis, chemical precipitation and ion exchange have some drawbacks which make them less suitable for removal of pollutants from water. Treatment techniques like chemical precipitation and coagulation-flocculation produce hazardous byproducts as waste and require high cost for operation[58]. Reverse osmosis is somehow effective while it is also expensive technique in terms of fueling, costly energy demand and high priced membrane[59]. Because of the limited applications of current water treatment technologies, it is now significant to develop and create novel and efficient materials at a low cost which offer improved characteristics, high efficiency and less cost.

Nanocomposites are proved to be an efficient and novel materials for the decontamination of water and strong alternatives for the removal of toxic contaminants[60].  Compared to conventional techniques, nanocomposites which are made up of nanoparticles embedded in a matrix, exhibit improved membrane filtration, catalytic activity, and adsorption properties[61]. Heavy metals, organic dyes, and microbes are just a few of the pollutants that nanocomposites can successfully remove due to their massive surface area, tailored chemical compositions, and effective extraction techniques[62, 63]. Different types of nanocomposites degrade different type of pollutants [24, 27, 34, 55, 64-74]. Metal oxide based nanocomposites like TiO2-ZnO, TiO2-Graphene, ZnO-Ag, Fe3O4 remove organic pollutants from water in the presence of light[75]. Carbon-based nanocomposites such as carbon nanotubes, graphene oxide exhibit a high potential to adsorb organic dyes and heavy metals[76-78]. Polymer-based nanocomposites (Chitosan- Fe3O4, PVA-TiO2, PVA-Ag) display antibacterial characteristics, making them useful for detoxification applications[79, 80].

 

Adsorption

Upto the start of 21st century, eradication of pollutant especially dyes and heavy metals involved only basic water purification processes such as equalization and sedimentation[81]. There is need to develop treatment methods of water that are more economical and reliable. Among the number of  available methods, adsorption has emerged as a superior, preferred and prominent technique[31]. The surface phenomenon in which accumulation of particular component at the surface or at the interface between two phases occurs is called adsorption[82]. Simple operation, high effectiveness[83], cost effective, no production of toxic byproducts[84], production of high quality treated effluent, resistance for harmful chemicals[85], small maintenance, exceptional versatility, [86], capability of treatment of highly concentrated colourants[31], regeneration and use of adsorbent again and again are some of the unique characteristics of adsorption process which make this process the best and the most reliable among all other methods available. Adsorbents may adsorb heavy metal ions present in water through chemical or physical attraction. Chemical adsorption is more reliable for the removal of heavy metals because heavy metals ions are strongly attracted towards functional groups present on the surface of the adsorbent[43].

 

Role of nanocomposite in water treatment through adsorption

Water contamination is increasing day-by-day and heavy metals are playing their role dangerously due to their toxic nature, chemical and physical stability, and bioaccumulation.  Nanocomposites are now appealing materials for the removal of heavy metals from water through adsorption because of their unique physiochemical characteristics. These nanocomposites can remove highly toxic heavy metals with high percentage removal at very low concentration[87].

  

Synthesis of nanocomposites

Nanocomposites are made up of matrix (polymer, metal) and nanofiller (nanomaterials, nanotubes). This interaction between matrix and nanofiller give unique properties to nanocomposites such as improved thermal. electrical, and mechanical properties. Nanocomposites can be synthesized by various ways, however, their synthesis methods are broadly divided into top down and bottom up approaches. Table 1 describes the comprehensive outlook of synthesis, properties, and applications of the nanocomposites types.

The top-down approach uses mechanical and physical techniques to break down bulk materials into nanoscale structures. Commonly employed methods include ball milling, laser ablation, and mechanical milling. For instance, mechanical milling reduces the size of bulk materials into nano-range while preserving their structural and chemical strength by using extremely powerful crushing. By directing high-energy lasers onto a substance and forcing it to evaporate into tiny particles, laser ablation produces nanoparticles[88]. Even though these techniques work smoothly, these methods frequently demand high amount of energy[89].  While the bottom-up approach employs chemical or biological processes to assemble nanostructures from atomic or molecular precursors. Common techniques include co-precipitation, sol-gel synthesis, and hydrothermal techniques. Sol-gel produces nanocomposites with uniform size and shape by hydrolyzing and condensing monomers. Metal oxide nanocomposites are synthesized most effectively by co-precipitation, whereas hydrothermal techniques produce homogeneous, highly crystalline nanostructures under controlled pressure and temperature[90].

 

Characterization of nanocomposites

Mechanical charcterization

Nanocomposites are characterized mechanicallly through various theoritical and empirical approaches. These techniques determine mechanical parameters of the nanocomposites. These analysing techniques include Compression analysis, tensile analysis, the Flexure analysis, the Hardness analysis, Dynamic Mechanical analysis (DMA), Universal testing machine (UTM), the Shear test, impact test and many others[91]. The durability of particular material in real world applications can be estimated from mechanical tests of various components. UTM determines compressive and tensile strength, whereas DMA investigates viscoelastic behavior under oscillatory stress. As nanocomposites are uniformly distributed, adding nano fillers to matrix often results in higher mechanical strength and stiffness. For example, graphene and the substrate material have a strong interfacial interaction, as a result, graphene oxide-based nanocomposites offer excellent tensile strength. A single test cannot assess mechanical strengths of target material since various materials interact differently to a particular set of conditions.

 

Thermal characterization

The aim of thermal characterization of nanocomposites is to examine how the materials behave under varying conditions of heat, temperature, and moisture in order to evaluate parameters such as melting points, coefficients of expansion, glass transition temperatures, dilations, heat stresses, strains, and thermomechanical characteristics, etc. Various experimental and theoretical investigations were conducted to test heat resistance and thermal stability of the materials. These tests include the Thermo-Gravimetric Analysis (TGA), Thermo-Mechanical Analysis (TMA), the Differential Scanning Calorimetry (DSC), the Hygroscopicity Test and the Melt Index Rheology Analysis (MI-RA)[91-93].

DSC determines crystallization points, glass transition, and melting points, giving insights into thermal changes. TGA examines loss in weight as an index of temperature, providing thermal degradation temperatures and material stability. Polymer-based nanocomposites often show enhanced heat stability because fillers hinder the mobility of the polymer chains. These characterizations are helpful in determining the suitability of these nanocomposite materials for industrials applications where temperature varies significantly. These tests are helpful in giving a broad picture of how the material would break down or transform under particular events.

 

Chemical characterization

Chemical composition, number and type of bonds, chemical stability and reactivity of the nanocomposites can be identified by various chemical characterization techniques. These techniques include X-Ray Diffraction (XRD), Scanning Electron Microscopy (SEM), Transmission Electron Microscopy (TEM), X-ray Absorption Spectroscopy (XAS), the Fourier Transform Infra-Red (FTIR) Spectroscopy[94], Electron-Paramagnetic Resonance (EPR) Spectroscopy, the Raman Spectroscopy and the Energy Dispersive Spectroscopy (EDS), Mass spectrometry, X-ray Photoelectron Spectroscopy (XPS)[95, 96].

FT-IR determines particular functional groups vibrations of nanocomposites [33, 35, 97-99] while XPS gives detail about composition and varying oxidation states. Glow discharge spectrometry and induced coupled plasma spectroscopy are 2 techniques that are currently effective in determining the deposited layer’s surface concentration[91]. These techniques are especially beneficial for understanding how chemical interactions, such as covalent bonds or hydrogen interactions, between nanomaterials and matrix components affect adsorption capacities in water treatment applications.

To optimize the performance and customize nanocomposites for particular uses, an intensive understanding of the mechanical, thermal, and chemical characteristics, achieved through integrating these methods, is necessary.

 

ADSORPTION MECHANISM OF HEAVY METALS USING NANOCOMPOSITES

Nanocomposites have showed high removal efficiency of heavy metals through adsorption process due to their unique properties such as large surface area, better selectivity, and high adsorption capacity. Table 2 shows adsorption capacity of different nanocomposites for heavy metals. Adsorption mechanism of heavy metals using nanocomposites involves physical and chemical adsorption approaches.  

In diffusion mechanism, heavy metals from solution move onto the surface of the adsorbent through diffusion and get adsorbed on the active sites (pores) of the nanocomposites materials (adsorbent). Weak Vander waal forces develop between heavy metals ions and adsorbent surface[100]. In porous nanocomposites, such as metal organic based nanocomposites, where diffusion through small pores is critical, this technique is commonly used. There are two stages of diffusion: intra-particle diffusion (movement within porous structures) and external diffusion (displacement to the outside surface of the material). Adsorptive removal of Pb(II) on activated CN tubes is example of surface adsorption[101].

Some nanocomposites have negatively charged functional group (-OH-, -COOH-, -NH2) on their surface which attract positively charged heavy metals ions in solution. The chemical reactions between nanocomposite and heavy metal ions are highly pH sensitive because the electrical charge on the surface of nanocomposite varies with pH. Electrostatic interaction between functional groups of nanocomposites and heavy metal ions cause removal of heavy metals from aqueous solution e.g. removal of Cu(II) through graphene oxide[102]. Chitosan-based nanocomposites effectively removed heavy metal from water due to interaction between NH2 and OH functional groups and heavy metals ions[103]. This mechanism is particularly useful for heavy metals with low concentration as electrostatic interaction increases rapidly at initial stage.

In ion exchange mechanism, Heavy metal ions in solution are replaced by positively charged ions such as Na+, K+, Mg+2 present on surface of the nanocomposite. These cations don’t cause water pollution.  This type of mechanism is very effective in layered nano range materials like zeolites and clay. These cations don’t cause water pollution. Na+ of zeolite are exchanged by Pb(II) is an example of ion exchange mechanism[104]. Due to its reversible nature, this mechanism is particular effective.

In complexation, some nanocomposites have functional groups such as carboxyl and amine on their surface which form coordination complex with heavy metal ions. This method is extremely specific to the selected metal’s and the nanocomposite’s chemical compositions. This phenomenon results in elimination of the heavy metals from water. In [105], thiol-functionalized carbon nanotubes form stable complexes with Hg(II) ions, radically enhancing their removal capability. Chitosan based nanocomposites form stable complexes with Cr(III) in water[106].

The redox mechanism involves a chemical reaction which takes place between heavy metal and surface of the adsorbent, making heavy metals less toxic. Surface of the nanocomposite acts as oxidizing or reducing agent. This method is specific with metals having variable oxidation state such as Cr(VI). Fe2O3  nanocomposite materials reduces Cr(IV) to Cr(III)[107].

 

CONCLUSION AND FUTURE OUTLOOK

Heavy metals contamination is common form of global water pollution. Several human and natural activities produce heavy metals such as Cu, Fe, Mo, Ni, Pb, Cd, Hg, Cr. All these metals cause serious issues for aquatic and terrestrial ecosystem. Addressing this issue requires efficient, scalable, and environmentally friendly solutions. Nanocomposites are highly efficient materials for removal of heavy metals from aqueous solution due to their high surface area, porosity, and multifunctional reactivity. The review highlights the exceptional adsorption capacities of nanocomposites like ZnO-CNT, GO-Fe3O4, MnO2-GO, CNF-Fe3O4, Ag-Al2O3, and TiO2-CeO2, which achieve removal efficiencies higher than 90% for several metals, including lead, cadmium, and chromium. Adsorption is superior technique because of high efficiency, affordability and reliability. Despite these advancements and developments, many challenges such as the high cost of synthesis, variability, and limited environmental sustainability of current nanocomposites remain significant. An interdisciplinary approach that combines innovations in material science with economical and environmentally friendly production techniques is needed to overcome these barriers. The future of water treatment proposes improved efficiency, lower cost, and environmental compatibility through the incorporation of nanocomposites with cutting-edge methods like photocatalysis or hybrid filtration methods.

In future, Nanocomposites have the potential to advance economical, effective, and ecological solutions for water purification. In order to reduce the impact on the environment, new research should focus on developing green synthesis techniques that make use of biopolymers, agricultural waste, and renewable resources. It will be significant to improve the adsorption capacity of nanocomposites through making structural changes such as enlarging their surface area, adjusting their pore size, and functionalizing their surfaces with certain chemical groups. Additionally, the effectiveness of water treatment could potentially be increased by incorporating nanocomposites into hybrid systems that include adsorption, photocatalysis, and modified filtration systems. Another critical area of attention is the life cycle analysis of these materials, emphasizing recyclability and biodegradability to reduce additional contamination. With the goal to scale up these breakthroughs for practical uses and make sure that future nanocomposites meet the objectives of environmental sustainability and economic growth, cooperation across the academic, industrial, and regulatory sectors will be crucial.

 

CONFLICT OF INTEREST

The authors declare that there is no conflict of interests regarding the publication of this manuscript.

1. Kılıç Z. The importance of water and conscious use of water. International Journal of Hydrology. 2020;4(5):239-241.
2. Fn C, Mf M. Factors Affecting Water Pollution: A Review. Journal of Ecosystem & Ecography. 2017;07(01).
3. Nonpoint Source Water Pollution. Environmental Engineering: Elsevier; 2003. p. 233-249.
4. Al-Asadi ST, Al-Qaim FF. Adsorption of Methylene Blue Dye from aqueous solution using low cost adsorbent: Kinetic, Isotherm Adsorption and Thermodynamic Studies. Research Square Platform LLC; 2023.
5. Batool M, Javed T, Wasim M, Zafar S, Din MI. Exploring the usability of Cedrus deodara sawdust for decontamination of wastewater containing crystal violet dye. Desalination and Water Treatment. 2021;224:433-448.
6. Ghzal Q, Javed T, Batool M. Potential of easily prepared low-cost rice husk biochar and burnt clay composite for the removal of methylene blue dye from contaminated water. Environmental Science: Water Research & Technology. 2023;9(11):2925-2941.
7. Kanwal F, Javed T, Hussain F, Wasim M, Batool M. Enhanced dye photodegradation through ZnO and ZnO-based photocatalysts doped with selective transition metals: a review. Environmental Technology Reviews. 2024;13(1):754-793.
8. Rafak SH, Jasim LS. Synthesis of novel bentonite/pectin-grafted-poly(crotonic acid-co-acrylic acid) hydrogel nanocomposite for adsorptive removal of safranin O dye from aqueous solution. International Journal of Environmental Analytical Chemistry. 2024:1-24.
9. Mannan HA, Nadeem R, Bibi S, Javed T, Javed I, Nazir A, et al. Mesoporous activated TiO 2 /based biochar synthesized from fish scales as a proficient adsorbent for deracination of heavy metals from industrial efflux. Journal of Dispersion Science and Technology. 2022;45(2):329-341.
10. Saadallah K, Ad C, Djedid M, Batool M, Benalia M, Saadallah S, Hamamda S. Potential of the Algerian pine tree bark for the adsorptive removal of methylene blue dye: Kinetics, isotherm and mechanism study. Journal of Dispersion Science and Technology. 2024:1-19.
11. Shah A, Arjunan A, Manning G, Batool M, Zakharova J, Hawkins AJ, et al. Sequential novel use of Moringa oleifera Lam., biochar, and sand to remove turbidity, E. coli, and heavy metals from drinking water. Cleaner Water. 2024;2:100050.
12. Roy H, Islam MS, Arifin MT, Firoz SH. Chitosan-ZnO decorated Moringa oleifera seed biochar for sequestration of methylene blue: Isotherms, kinetics, and response surface analysis. Environmental Nanotechnology, Monitoring & Management. 2022;18:100752.
13. Shah A, Arjunan A, Thumma A, Zakharova J, Bolarinwa T, Devi S, Batool M. Adsorptive removal of arsenic from drinking water using KOH-modified sewage sludge-derived biochar. Cleaner Water. 2024;2:100022.
14. Shah A, Zakharova J, Batool M, Coley MP, Arjunan A, Hawkins AJ, et al. Removal of cadmium and zinc from water using sewage sludge-derived biochar. Sustainable Chemistry for the Environment. 2024;6:100118.
15. Femina Carolin C, Kumar PS, Joshiba GJ, Madhesh P, Ramamurthy R. Sustainable strategy for the enhancement of hazardous aromatic amine degradation using lipopeptide biosurfactant isolated from Brevibacterium casei. Journal of Hazardous Materials. 2021;408:124943.
16. Dwivedi OP. India : Pollution Control Policy and Programmes. International Review of Administrative Sciences. 1977;43(2):123-133.
17. Zamora-Ledezma C, Negrete-Bolagay D, Figueroa F, Zamora-Ledezma E, Ni M, Alexis F, Guerrero VH. Heavy metal water pollution: A fresh look about hazards, novel and conventional remediation methods. Environmental Technology & Innovation. 2021;22:101504.
18. Villarín MC, Merel S. Paradigm shifts and current challenges in wastewater management. Journal of Hazardous Materials. 2020;390:122139.
19. Muhammad Ekramul Mahmud HN, Huq AKO, Yahya Rb. The removal of heavy metal ions from wastewater/aqueous solution using polypyrrole-based adsorbents: a review. RSC Advances. 2016;6(18):14778-14791.
20. Miao J-L, Ren J-Q, Li H-J, Wu D-G, Wu Y-C. Mesoporous crosslinked chitosan-activated clinoptilolite biocomposite for the removal of anionic and cationic dyes. Colloids and Surfaces B: Biointerfaces. 2022;216:112579.
21. Majdoubi H, Alqadami AA, Billah REK, Otero M, Jeon B-H, Hannache H, et al. Chitin-Based Magnesium Oxide Biocomposite for the Removal of Methyl Orange from Water. International journal of environmental research and public health. 2023;20(1):831.
22. Stobel Christy EJ, Pius A. Performance of metal free g-C3N4 reinforced graphene oxide bio-composite for the removal of persistent dyes. Environmental Chemistry and Ecotoxicology. 2021;3:220-233.
23. Ayni S, Sabet M, Mahdi MA, Abdulsahib WK, Taher AM, Zareie N, Salavati-Niasari M. Synthesis of flower-like and hexagonal PbWO4 nanostructures via the co-precipitation method and study of their photocatalytic activity in the degradation of rhodamine B. Biomass Conversion and Biorefinery. 2022;14(3):3477-3487.
24. Al-Harby NF, Albahly EF, Mohamed NA. Kinetics, Isotherm and Thermodynamic Studies for Efficient Adsorption of Congo Red Dye from Aqueous Solution onto Novel Cyanoguanidine-Modified Chitosan Adsorbent. Polymers. 2021;13(24):4446.
25. Mahmood Taher A, Ali Kadhim Kyhoiesh H, Shakir Waheeb A, Al-Adilee KJ, Jasim LS. Synthesis, characterization, biological activity, and modelling protein docking of divalent, trivalent, and tetravalent metal ion complexes of new azo dye ligand (N,N,O) derived from benzimidazole. Results in Chemistry. 2024;12:101911.
26. The value of two onset determination of anti-H.pylori IgM antibody in patients with dyspepsia in Iraq. International Journal of Pharmaceutical Research. 2020;12(02).
27. Bayati-Komitaki N, Ganduh SH, Alzaidy AH, Salavati-Niasari M. A comprehensive review of Co3O nanostructures in cancer: Synthesis, characterization, reactive oxygen species mechanisms, and therapeutic applications. Biomedicine & Pharmacotherapy. 2024;180:117457.
28. The value of iron supplementation to children with Helicobacter pylori infection in Iraq: a cross-sectional study. International Journal of Pharmaceutical Research. 2020;12(02).
29. Marghzari S, Sasani M, Kaykhaii M, Sargazi M, Hashemi M. Simultaneous elimination of Malachite Green, Rhodamine B and Cresol Red from aqueous sample with Sistan sand, optimized by Taguchi L16 and Plackett-Burman experiment design methods. Chemistry Central journal. 2018;12(1):116-116.
30. Pai S, Kini MS, Selvaraj R. A review on adsorptive removal of dyes from wastewater by hydroxyapatite nanocomposites. Environmental Science and Pollution Research. 2019;28(10):11835-11849.
31. Kausar F, Javed T, Khalid N, Mirza ML. Decontamination of silver ions from aqueous solution using coconut coir. Desalination and Water Treatment. 2023;283:118-129.
32. Shah A, Arjunan A, Manning G, Zakharova J, Andraulaki I, Batool M. The effect of dose, settling time, shelf life, storage temperature and extractant on Moringa oleifera Lam. protein coagulation efficiency. Environmental Nanotechnology, Monitoring & Management. 2024;21:100919.
33. Arshad R, Javed T, Thumma A. Exploring the efficiency of sodium alginate beads and Cedrus deodara sawdust for adsorptive removal of crystal violet dye. Journal of Dispersion Science and Technology. 2023;45(12):2330-2343.
34. Javed T, Kausar F, Zawar MD, Khalid N, Thumma A, Ismail A, et al. Investigating the adsorption potential of coconut coir as an economical adsorbent for decontamination of lanthanum ion from aqueous solution. Journal of Dispersion Science and Technology. 2024:1-12.
35. Javed T, Thumma A, Uddin AN, Akhter R, Babar Taj M, Zafar S, et al. Batch adsorption study of Congo Red dye using unmodified Azadirachta indica leaves: isotherms and kinetics. Water Practice & Technology. 2024;19(2):546-566.
36. Rehman H, Javed T, Thumma A, Uddin AN, Singh N, Baig MM, et al. Potential of easily available low-cost raw cotton for the elimination of methylene blue dye from polluted water. Desalination and Water Treatment. 2024;318:100319.
37. Bukhari A, Javed T, Haider MN. Adsorptive exclusion of crystal violet dye from wastewater by using fish scales as an adsorbent. Journal of Dispersion Science and Technology. 2022;44(11):2081-2092.
38. Imran MS, Javed T, Areej I, Haider MN. Sequestration of crystal violet dye from wastewater using low-cost coconut husk as a potential adsorbent. Water Science and Technology. 2022;85(8):2295-2317.
39. Urooj H, Javed T, Taj MB, Nouman Haider M. Adsorption of crystal violet dye from wastewater on Phyllanthus emblica fruit (PEF) powder: kinetic and thermodynamic. International Journal of Environmental Analytical Chemistry. 2023;104(19):7474-7499.
40. Çetin M, Ozudogru Y. Removal of malachite green dye by adsorption onto chitosan-montmorillonite nanocomposite: Kinetic, thermodynamic and equilibrium studies. Journal of the Chinese Chemical Society. 2025.
41. Timothy Na, Tagui Williams E. Environmental Pollution by Heavy Metal: An Overview. International Journal of Environmental Chemistry. 2019;3(2):72.
42. Rao H, Rao L, Chanakya HN. Fate of Heavy Metals in Sewage and Polluted Water Bodies. Current Science. 2021;121(1):109.
43. Khulbe KC, Matsuura T. Removal of heavy metals and pollutants by membrane adsorption techniques. Applied Water Science. 2018;8(1).
44. Edelstein M, Ben-Hur M. Heavy metals and metalloids: Sources, risks and strategies to reduce their accumulation in horticultural crops. Scientia Horticulturae. 2018;234:431-444.
45. Zwolak A, Sarzyńska M, Szpyrka E, Stawarczyk K. Sources of Soil Pollution by Heavy Metals and Their Accumulation in Vegetables: a Review. Water, Air, & Soil Pollution. 2019;230(7).
46. Masindi V, Muedi KL. Environmental Contamination by Heavy Metals. Heavy Metals: InTech; 2018.
47. Pratush A, Kumar A, Hu Z. Adverse effect of heavy metals (As, Pb, Hg, and Cr) on health and their bioremediation strategies: a review. International Microbiology. 2018;21(3):97-106.
48. Azimi A, Azari A, Rezakazemi M, Ansarpour M. Removal of Heavy Metals from Industrial Wastewaters: A Review. ChemBioEng Reviews. 2017;4(1):37-59.
49. Rehman K, Fatima F, Waheed I, Akash MSH. Prevalence of exposure of heavy metals and their impact on health consequences. Journal of Cellular Biochemistry. 2017;119(1):157-184.
50. Triassi M, Cerino P, Montuori P, Pizzolante A, Trama U, Nicodemo F, et al. Heavy Metals in Groundwater of Southern Italy: Occurrence and Potential Adverse Effects on the Environment and Human Health. International journal of environmental research and public health. 2023;20(3):1693.
51. Zahra N. Perilous effects of heavy metals contamination on human health. Pakistan Journal of Analytical & Environmental Chemistry. 2017;18(1):1-17.
52. Jaiswal A, Verma A, Jaiswal P. Detrimental Effects of Heavy Metals in Soil, Plants, and Aquatic Ecosystems and in Humans. Journal of Environmental Pathology, Toxicology and Oncology. 2018;37(3):183-197.
53. Piaia L, Salmoria GV, Hotza D. Additive Manufactured Nanocomposites for Bone Tissue Engineering Applications: an Overview. Materials Research. 2020;23(1).
54. Gidde ND, Nitalikar MM, Raut ID. Nanocomposites: A Review on Current Status. Asian Journal of Pharmacy and Technology. 2021:231-237.
55. Shakerimoghaddam A, Majeed HJ, Hashim AJ, Abed MJ, Jasim LS, Salavati-Niasari M. Green synthesis and characterization of NiO/Hydroxyapatite nanocomposites in the presence of peppermint extract and investigation of their antibacterial activities against Pseudomonas aeruginosa and Staphylococcus aureus. Results in Chemistry. 2025;13:101947.
56. Mittal H, Al Alili A, Alhassan SM. High efficiency removal of methylene blue dye using κ-carrageenan-poly(acrylamide-co-methacrylic acid)/AQSOA-Z05 zeolite hydrogel composites. Cellulose. 2020;27(14):8269-8285.
57. Khan E, Khan S, Khan A. Polymer nanocomposites for biomedical applications. Smart Polymer Nanocomposites: Elsevier; 2023. p. 279-303.
58. Wishart DS, Guo A, Oler E, Wang F, Anjum A, Peters H, et al. HMDB 5.0: the Human Metabolome Database for 2022. Nucleic acids research. 2022;50(D1):D622-D631.
59. Qasem NAA, Mohammed RH, Lawal DU. Removal of heavy metal ions from wastewater: a comprehensive and critical review. npj Clean Water. 2021;4(1).
60. Khodakarami M, Bagheri M. Recent advances in synthesis and application of polymer nanocomposites for water and wastewater treatment. Journal of Cleaner Production. 2021;296:126404.
61. Xia C, Li X, Wu Y, Suharti S, Unpaprom Y, Pugazhendhi A. A review on pollutants remediation competence of nanocomposites on contaminated water. Environmental Research. 2023;222:115318.
62. Modi S, Balmiki V, Kaushik V, Mohan C, Kumar R, Ravikanth P, Dayawati. Green Synthesis of Nanocomposite Membranes for Sustainable Water Filtration. E3S Web of Conferences. 2024;511:01015.
63. Annu, Mittal M, Tripathi S, Shin DK. Biopolymeric Nanocomposites for Wastewater Remediation: An Overview on Recent Progress and Challenges. Polymers. 2024;16(2):294.
64. Majeed HJ, Idrees TJ, Mahdi MA, Abed MJ, Batool M, Yousefi SR, et al. Synthesis and application of novel sodium carboxy methyl cellulose-g-poly acrylic acid carbon dots hydrogel nanocomposite (NaCMC-g-PAAc/ CDs) for adsorptive removal of malachite green dye. Desalination and Water Treatment. 2024;320:100822.
65. Jamdar M, Monsef R, Ganduh SH, Dawi EA, Jasim LS, Salavati-Niasari M. Unraveling the potential of sonochemically achieved DyMnO3/Dy2O3 nanocomposites as highly efficient visible-light-driven photocatalysts in decolorization of organic contamination. Ecotoxicology and Environmental Safety. 2024;269:115801.
66. Sajeesh S, Sharma CP. Mucoadhesive hydrogel microparticles based on poly (methacrylic acid-vinyl pyrrolidone)-chitosan for oral drug delivery. Drug Delivery. 2010;18(4):227-235.
67. Mahde BW, Sultan AM, Mahdi MA, Jasim LS. Kinetic Adsorption and Release Study of Sulfadiazine Hydrochloride Drug from Aqueous Solutions on GO/P(AA-AM-MCC) Composite. INTERNATIONAL JOURNAL OF DRUG DELIVERY TECHNOLOGY. 2022;12(04):1583-1589.
68. Hiroki A, Taguchi M. Development of Environmentally Friendly Cellulose Derivative-Based Hydrogels for Contact Lenses Using a Radiation Crosslinking Technique. Applied Sciences. 2021;11(19):9168.
69. Atyaa AI, Radhy ND, Jasim LS. Synthesis and Characterization of Graphene Oxide/Hydrogel Composites and Their Applications to Adsorptive Removal Congo Red from Aqueous Solution. Journal of Physics: Conference Series. 2019;1234(1):012095.
70. Hosseini M, Ghanbari M, Alzaidy AH, Dawi EA, Mahdi MA, Jasim LS, et al. Synthesis and characterization of Fe2SiO4/Fe2O3/g-C3N4 ternary heterojunction photocatalyst with enhanced photocatalytic activity under visible light. International Journal of Hydrogen Energy. 2024;60:1370-1382.
71. Kianipour S, Razavi FS, Hajizadeh-Oghaz M, Abdulsahib WK, Mahdi MA, Jasim LS, Salavati-Niasari M. The synthesis of the P/N-type NdCoO3/g-C3N4 nano-heterojunction as a high-performance photocatalyst for the enhanced photocatalytic degradation of pollutants under visible-light irradiation. Arabian Journal of Chemistry. 2022;15(6):103840.
72. Mhammed Alzayd AA, Atyaa AI, Radhy ND, Jasim Al-Hayder LS. A new adsorption material based GO/PVP/AAc composite hydrogel characterization, study kinetic and thermodynamic to removal Atenolol drug from wast water. IOP Conference Series: Materials Science and Engineering. 2020;928(6):062023.
73. Ghazi HH, Aljeboree AM. Synthetic Water-Gel Crystals (Orbeez Balls) as Environmentally Friendly Adsorbent for Removal of Toxic Brilliant Green Dye From Aqueous Solutions. Asian Journal of Water, Environment and Pollution. 2024;21(3):53-60.
74. Mahdi MA, Oroumi G, Samimi F, Dawi EA, Abed MJ, Alzaidy AH, et al. Tailoring the innovative Lu2CrMnO6 double perovskite nanostructure as an efficient electrode materials for electrochemical hydrogen storage application. Journal of Energy Storage. 2024;88:111660.
75. Origin of the Improved Photoelectrochemical and Photocatalytic Activity in a ZnO-TiO2 Nanohybrid Revealed by Experimental and Density Functional Theory Studies. American Chemical Society (ACS).
76. Ali Khan M, Govindasamy R, Ahmad A, Siddiqui MR, Alshareef SA, Hakami AAH, Rafatullah M. Carbon Based Polymeric Nanocomposites for Dye Adsorption: Synthesis, Characterization, and Application. Polymers. 2021;13(3):419.
77. Mandal S, Mallapur S, Reddy M, Singh JK, Lee D-E, Park T. An Overview on Graphene-Metal Oxide Semiconductor Nanocomposite: A Promising Platform for Visible Light Photocatalytic Activity for the Treatment of Various Pollutants in Aqueous Medium. Molecules (Basel, Switzerland). 2020;25(22):5380.
78. Lang J, Takahashi K, Kubo M, Shimada M. Preparation of TiO2-CNT-Ag Ternary Composite Film with Enhanced Photocatalytic Activity via Plasma-Enhanced Chemical Vapor Deposition. Catalysts. 2022;12(5):508.
79. Zaferani SH. Introduction of polymer-based nanocomposites. Polymer-based Nanocomposites for Energy and Environmental Applications: Elsevier; 2018. p. 1-25.
80. Prateek, Thakur VK, Gupta RK. Recent Progress on Ferroelectric Polymer-Based Nanocomposites for High Energy Density Capacitors: Synthesis, Dielectric Properties, and Future Aspects. Chemical Reviews. 2016;116(7):4260-4317.
81. Katheresan V, Kansedo J, Lau SY. Efficiency of various recent wastewater dye removal methods: A review. Journal of Environmental Chemical Engineering. 2018;6(4):4676-4697.
82. Abdollahi SB. A New Approach for Analysis of Adsorption from Liquid Phase: A Critical Review. Journal of Pollution Effects & Control. 2015;03(02).
83. Kaykhaii M, Sasani M, Marghzari S. Removal of Dyes from the Environment by Adsorption Process. Chemical and Materials Engineering. 2018;6(2):31-35.
84. Sposito G. Soil Adsorption Phenomena. The Chemistry of Soils: Oxford University Press; 2016.
85. Wang M, Chen L, Zhang Z. Potential applications of alginate oligosaccharides for biomedicine – A mini review. Carbohydrate Polymers. 2021;271:118408.
86. Homagai PL, Poudel R, Poudel S, Bhattarai A. Adsorption and removal of crystal violet dye from aqueous solution by modified rice husk. Heliyon. 2022;8(4):e09261-e09261.
87. Lee A, Elam JW, Darling SB. Membrane materials for water purification: design, development, and application. Environmental Science: Water Research & Technology. 2016;2(1):17-42.
88. Zhou Z, Ren L, Zhang L, Zhong J, Xiao Y, Jia Z, et al. Heightened Innate Immune Responses in the Respiratory Tract of COVID-19 Patients. Cell host & microbe. 2020;27(6):883-890.e882.
89. Safiri S, Kolahi A-A, Naghavi M, Global Burden of Disease Bladder Cancer C. Global, regional and national burden of bladder cancer and its attributable risk factors in 204 countries and territories, 1990-2019: a systematic analysis for the Global Burden of Disease study 2019. BMJ global health. 2021;6(11):e004128.
90. Wang K, Aktas YD, Malki-Epshtein L, Wu D, Ammar Bin Abdullah MF. Mapping the city scale anthropogenic heat emissions from buildings in Kuala Lumpur through a top-down and a bottom-up approach. Sustainable Cities and Society. 2022;76:103443.
91. Kotal M, Bhowmick AK. Polymer nanocomposites from modified clays: Recent advances and challenges. Progress in Polymer Science. 2015;51:127-187.
92. Bokov D, Turki Jalil A, Chupradit S, Suksatan W, Javed Ansari M, Shewael IH, et al. Nanomaterial by Sol-Gel Method: Synthesis and Application. Advances in Materials Science and Engineering. 2021;2021(1).
93. Cao C, Killips A, Li X. Advances in the Science and Engineering of Metal Matrix Nanocomposites: A Review. Advanced Engineering Materials. 2024;26(20).
94. Hao R, Xing R, Xu Z, Hou Y, Gao S, Sun S. Synthesis, Functionalization, and Biomedical Applications of Multifunctional Magnetic Nanoparticles. Advanced Materials. 2010;22(25):2729-2742.
95. Ding L, Yu Z-D, Wang X-Y, Yao Z-F, Lu Y, Yang C-Y, et al. Polymer Semiconductors: Synthesis, Processing, and Applications. Chemical Reviews. 2023;123(12):7421-7497.
96. Xiong R, Grant AM, Ma R, Zhang S, Tsukruk VV. Naturally-derived biopolymer nanocomposites: Interfacial design, properties and emerging applications. Materials Science and Engineering: R: Reports. 2018;125:1-41.
97. Vinyas M, Athul SJ, Harursampath D, Loja M, Nguyen Thoi T. A comprehensive review on analysis of nanocomposites: from manufacturing to properties characterization. Materials Research Express. 2019;6(9):092002.
98. Saadallah S, Cablé A, Hamamda S, Chetehouna K, Sahli M, Boubertakh A, et al. Structural and thermal characterization of multiwall carbon nanotubes (MWCNTs) / aluminum (Al) nanocomposites. Composites Part B: Engineering. 2018;151:232-236.
99. Maher H, Rocky KA, Bassiouny R, Saha BB. Synthesis and thermal characterization of paraffin-based nanocomposites for thermal energy storage applications. Thermal Science and Engineering Progress. 2021;22:100797.
100. Enders AA, North NM, Fensore CM, Velez-Alvarez J, Allen HC. Functional Group Identification for FTIR Spectra Using Image-Based Machine Learning Models. Analytical Chemistry. 2021;93(28):9711-9718.
101. Saletnik A, Saletnik B, Puchalski C. Overview of Popular Techniques of Raman Spectroscopy and Their Potential in the Study of Plant Tissues. Molecules (Basel, Switzerland). 2021;26(6):1537.
102. Korin E, Froumin N, Cohen S. Surface Analysis of Nanocomplexes by X-ray Photoelectron Spectroscopy (XPS). ACS Biomaterials Science & Engineering. 2017;3(6):882-889.
103. Batool M, Abid MA, Javed T, Haider MN. Applications of biodegradable polymers and ceramics for bone regeneration: a mini-review. International Journal of Polymeric Materials and Polymeric Biomaterials. 2024;74(1):39-53.
104. Batool M, Haider MN, Javed T. Applications of Spectroscopic Techniques for Characterization of Polymer Nanocomposite: A Review. Journal of Inorganic and Organometallic Polymers and Materials. 2022;32(12):4478-4503.
105. Nipaa ST, Rahman MW, Sahaa R, Hasana MM, Deb A. Jute stick powder as a potential low-cost adsorbent to uptake methylene blue from dye enriched wastewater. Desalination and Water Treatment. 2019;153:279-287.
106. Zhang L, Su T, Luo Z, Xu B, Yao W, Zhou M, et al. A graphene-based porous composite hydrogel for efficient heavy metal ions removal from wastewater. Separation and Purification Technology. 2023;305:122484.
107. Das S, Chakraborty J, Chatterjee S, Kumar H. Prospects of biosynthesized nanomaterials for the remediation of organic and inorganic environmental contaminants. Environmental Science: Nano. 2018;5(12):2784-2808.
108. Fu F, Wang Q. Removal of heavy metal ions from wastewaters: A review. Journal of Environmental Management. 2011;92(3):407-418.
109. Karthik R, Meenakshi S. Removal of Pb(II) and Cd(II) ions from aqueous solution using polyaniline grafted chitosan. Chemical Engineering Journal. 2015;263:168-177.
110. Pang T, Yang X, Yuan C, Elzatahry AA, Alghamdi A, He X, et al. Recent advance in synthesis and application of heteroatom zeolites. Chinese Chemical Letters. 2021;32(1):328-338.
111. Nayak T, Pathan A. Environmental remediation and application of carbon-based nanomaterials in the treatment of heavy metal-contaminated water: A review. Materials Today: Proceedings. 2023;92:1659-1670.
112. Bashir K, Jamil F, Iqbal MA, Nazir S, Shoukat US, Bashir A, et al. Detection of different chemical moieties in aqueous media by luminescent Europium as sensor. Reviews in Inorganic Chemistry. 2023;43(4):547-560.
113. Shaheen SM, Wang J, Baumann K, Ahmed AA, Hsu L-C, Liu Y-T, et al. Stepwise redox changes alter the speciation and mobilization of phosphorus in hydromorphic soils. Chemosphere. 2022;288:132652.
114. Al-Gheethi A, Ma NL, Rupani PF, Sultana N, Yaakob MA, Mohamed RMSR, Soon CF. Biowastes of slaughterhouses and wet markets: an overview of waste management for disease prevention. Environmental Science and Pollution Research International. 2023;30(28):71780-71793.
115. Bashir S, Hina M, Iqbal J, Rajpar AH, Mujtaba MA, Alghamdi NA, et al. Fundamental Concepts of Hydrogels: Synthesis, Properties, and Their Applications. Polymers. 2020;12(11):2702.
116. Yang Q, Qiu Q, Shi Y, Wang J, Chen F, Yang J, et al. Determination of strobilurin fungicides residual in vegetables based on amino modified magnetic graphene oxide solid phase extraction coupled with GC–MS/MS. Journal of Chromatography A. 2025;1739:465455.
117. Das S, Ranjan P, Chakraborty T. Carbon-Based Nanomaterials for Energy Storage: A Review. Carbon Composites: Apple Academic Press; 2023. p. 117-134.
118. Zhuang M, Achmon Y, Cao Y, Liang X, Chen L, Wang H, et al. Distribution of antibiotic resistance genes in the environment. Environmental Pollution. 2021;285:117402.
119. Lyu Y, Xu J, Cao Q, Zhou Z, Hu W, Liu X. Highly efficient removal of toluene over Cu-V oxides modified γ-Al2O3 in the presence of SO2. Journal of Hazardous Materials. 2022;436:129041.
120. Prakash O, Verma D, Singh PC. Exploring enzyme-immobilized MOFs and their application potential: biosensing, biocatalysis, targeted drug delivery and cancer therapy. Journal of Materials Chemistry B. 2024;12(40):10198-10214.
121. Zhao B, Ni C, Gao R, Wang Y, Yang L, Wei J, et al. Recapitulation of SARS-CoV-2 infection and cholangiocyte damage with human liver ductal organoids. Protein & cell. 2020;11(10):771-775.
122. Liu L, Iketani S, Guo Y, Chan JFW, Wang M, Liu L, et al. Striking antibody evasion manifested by the Omicron variant of SARS-CoV-2. Nature. 2021;602(7898):676-681.
123. Narmani A, Jafari SM. Chitosan-based nanodelivery systems for cancer therapy: Recent advances. Carbohydrate Polymers. 2021;272:118464.
124. Ponomarev N, Pastushok O, Repo E, Doshi B, Sillanpää M. Lignin-Based Magnesium Hydroxide Nanocomposite. Synthesis and Application for the Removal of Potentially Toxic Metals from Aqueous Solution. ACS Applied Nano Materials. 2019;2(9):5492-5503.