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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Nanotechnol.</journal-id>
<journal-title-group>
<journal-title>Frontiers in Nanotechnology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Nanotechnol.</abbrev-journal-title>
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<issn pub-type="epub">2673-3013</issn>
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<article-id pub-id-type="publisher-id">1751841</article-id>
<article-id pub-id-type="doi">10.3389/fnano.2026.1751841</article-id>
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<subj-group subj-group-type="heading">
<subject>Review</subject>
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<title-group>
<article-title>Green algae-based sustainable nanoparticles: cutting-edge applications for sustainable development goals benchmark</article-title>
<alt-title alt-title-type="left-running-head">Das et al.</alt-title>
<alt-title alt-title-type="right-running-head">
<ext-link ext-link-type="uri" xlink:href="https://doi.org/10.3389/fnano.2026.1751841">10.3389/fnano.2026.1751841</ext-link>
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<contrib-group>
<contrib contrib-type="author" equal-contrib="yes">
<name>
<surname>Das</surname>
<given-names>Mautushi</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>&#x2020;</sup>
</xref>
<xref ref-type="author-notes" rid="fn002">
<sup>&#x2021;</sup>
</xref>
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<contrib contrib-type="author" equal-contrib="yes">
<name>
<surname>Mohanta</surname>
<given-names>Tapan Kumar</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>&#x2020;</sup>
</xref>
<xref ref-type="author-notes" rid="fn002">
<sup>&#x2021;</sup>
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<contrib contrib-type="author">
<name>
<surname>Sangma</surname>
<given-names>Marchia K.</given-names>
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<xref ref-type="aff" rid="aff1">
<sup>1</sup>
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<name>
<surname>Semy</surname>
<given-names>Khikeya</given-names>
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<xref ref-type="aff" rid="aff4">
<sup>4</sup>
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<name>
<surname>Mishra</surname>
<given-names>Bishwambhar</given-names>
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<xref ref-type="aff" rid="aff5">
<sup>5</sup>
</xref>
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<sup>6</sup>
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<given-names>Nanaocha</given-names>
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<xref ref-type="aff" rid="aff7">
<sup>7</sup>
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<given-names>Yugal Kishore</given-names>
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<xref ref-type="aff" rid="aff8">
<sup>8</sup>
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<xref ref-type="aff" rid="aff9">
<sup>9</sup>
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<aff id="aff1">
<label>1</label>
<institution>Department of Botany, University of Science and Technology Meghalaya</institution>, <city>Baridua</city>, <state>Meghalaya</state>, <country country="IN">India</country>
</aff>
<aff id="aff2">
<label>2</label>
<institution>Department of Botany, Captain Williamson Sangma State University</institution>, <city>Tura</city>, <state>Meghalaya</state>, <country country="IN">India</country>
</aff>
<aff id="aff3">
<label>3</label>
<institution>Department of Genetic Research, Institute For Medical Research and Consultation, Imam Abdulrahman Bin Faisal University</institution>, <city>Dammam</city>, <country country="SA">Saudi Arabia</country>
</aff>
<aff id="aff4">
<label>4</label>
<institution>Department of Botany, New Model College</institution>, <city>Nagaland</city>, <country country="IN">India</country>
</aff>
<aff id="aff5">
<label>5</label>
<institution>Department of Biotechnology, Chaitanya Bharathi Institute of Technology (CBIT)</institution>, <city>Hyderabad</city>, <state>Telangana</state>, <country country="IN">India</country>
</aff>
<aff id="aff6">
<label>6</label>
<institution>Department of Food Technology, School of Agriculture, Dev Bhoomi Uttarakhand University</institution>, <city>Dehradun</city>, <state>Uttarakhand</state>, <country country="IN">India</country>
</aff>
<aff id="aff7">
<label>7</label>
<institution>Institute of Bioresources and Sustainable Development</institution>, <city>Imphal</city>, <state>Manipur</state>, <country country="IN">India</country>
</aff>
<aff id="aff8">
<label>8</label>
<institution>Nano-biotechnology and Translational Knowledge Laboratory, Department of Applied Biology, University of Science and Technology Meghalaya</institution>, <city>Baridua</city>, <state>Meghalaya</state>, <country country="IN">India</country>
</aff>
<aff id="aff9">
<label>9</label>
<institution>Centre for Herbal Pharmacology and Environmental Sustainability, Chettinad Hospital and Research Institute, Chettinad Academy of Research and Education</institution>, <city>Kelambakkam</city>, <state>Tamil Nadu</state>, <country country="IN">India</country>
</aff>
<author-notes>
<corresp id="c001">
<label>&#x2a;</label>Correspondence: Yugal Kishore Mohanta, <email xlink:href="mailto:ykmohanta@gmail.com">ykmohanta@gmail.com</email>; Nanaocha Sharma, <email xlink:href="mailto:sharma.nanaocha@gmail.com">sharma.nanaocha@gmail.com</email>
</corresp>
<fn fn-type="present-address" id="fn001">
<label>&#x2020;</label>
<p>
<bold>Present address:</bold> Mautushi Das, Captain Williamson Sangma State University, Meghalaya, India,</p>
</fn>
<fn fn-type="equal" id="fn002">
<label>&#x2021;</label>
<p>These authors have contributed equally to this work</p>
</fn>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-03-04">
<day>04</day>
<month>03</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2026</year>
</pub-date>
<volume>8</volume>
<elocation-id>1751841</elocation-id>
<history>
<date date-type="received">
<day>22</day>
<month>11</month>
<year>2025</year>
</date>
<date date-type="rev-recd">
<day>03</day>
<month>01</month>
<year>2026</year>
</date>
<date date-type="accepted">
<day>13</day>
<month>01</month>
<year>2026</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2026 Das, Mohanta, Sangma, Semy, Mishra, Rustagi, Sharma and Mohanta.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Das, Mohanta, Sangma, Semy, Mishra, Rustagi, Sharma and Mohanta</copyright-holder>
<license>
<ali:license_ref start_date="2026-03-04">https://creativecommons.org/licenses/by/4.0/</ali:license_ref>
<license-p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</license-p>
</license>
</permissions>
<abstract>
<p>Green algae, a diverse and abundant bioresource, have emerged as a sustainable platform for synthesizing nanoparticles (NPs) with wide-ranging applications. This review paper involves the reduction of metal salts by biological factors such as algae, inducing nanoparticles with unique properties, highlighting their eco-friendly synthesis, unique physicochemical properties, and multifaceted applications in biomedicine, agriculture, environmental remediation, and food technology. Algae-mediated NPs exhibit significant antimicrobial, antioxidant, anticancer, and catalytic properties, making them valuable for drug delivery, water purification, and biofuel production. From the 17 goals of SDGs, the role of algae is emphasized, notably in potable water safe to drink (SDG 6), renewable and accessible energy sources (SDG 7), hunger eradication (SDG 2), and climate mitigation (SDG 13). Nanomaterials hold great promise across various applications, yet they face significant challenges. Key issues include scalability for mass production, ensuring economic viability, and navigating complex regulatory landscapes that can hinder their development and implementation. Future research aims to optimize production methods, enhance biocompatibility, and expand applications in nanotechnology. Green algae-based NPs represent a promising, sustainable alternative to conventional nanomaterials, offering innovative solutions for global environmental and health challenges.</p>
</abstract>
<abstract abstract-type="graphical">
<title>Graphical Abstract</title>
<p>
<fig>
<graphic xlink:href="FNANO_fnano-2026-1751841_wc_abs.tif" position="anchor">
<alt-text content-type="machine-generated">Green algae lead to nanoparticle synthesis, followed by characterization involving porosity, surface charge, shape, and size distribution. Various nanoparticles like AuNPs and AgNPs are illustrated, linked to applications such as drug delivery, antibacterial, anticancer, antiviral, antifungal, haemolytic activity, and nano-bioremediation. These applications relate to Sustainable Development Goals 2, 6, 7, 13.</alt-text>
</graphic>
</fig>
</p>
</abstract>
<kwd-group>
<kwd>biomedicine</kwd>
<kwd>bioremediation</kwd>
<kwd>green algae</kwd>
<kwd>green synthesis</kwd>
<kwd>nanoparticles</kwd>
<kwd>sustainable development goals</kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was not received for this work and/or its publication.</funding-statement>
</funding-group>
<counts>
<fig-count count="8"/>
<table-count count="5"/>
<equation-count count="0"/>
<ref-count count="114"/>
<page-count count="22"/>
</counts>
<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Nanofabrication</meta-value>
</custom-meta>
</custom-meta-group>
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</front>
<body>
<sec sec-type="intro" id="s1">
<label>1</label>
<title>Introduction</title>
<p>Sustainable nanomaterials represent a groundbreaking advancement in materials science, offering eco-friendly solutions to global challenges while minimizing environmental impact (<xref ref-type="bibr" rid="B41">Gupta et al., 2023</xref>). A sustainable nanomaterial is a nanoscale material designed and produced in a way that meets human needs while minimizing harm to the environment and human health, using renewable resources, low energy, and non-toxic processes, and remaining safe, efficient, and recyclable throughout its entire life cycle. These materials, usually varying from 1 to 100 nano-sized, show distinct characteristics that make them invaluable across multiple sectors. Their sustainability stems from green synthesis methods using biological systems, renewable resources, and energy-efficient processes (<xref ref-type="bibr" rid="B97">Tonelli et al., 2023</xref>). In environmental applications, sustainable nanomaterials enable highly efficient water purification through photocatalytic degradation of contaminants and selective metal detoxification (<xref ref-type="bibr" rid="B37">Feisal et al., 2024</xref>). The energy sector benefits from their use in next-generation solar cells and energy storage devices, where they enhance efficiency while reducing material usage (<xref ref-type="bibr" rid="B46">Hussein, 2023</xref>). Biomedical applications include targeted drug delivery systems that minimize aftereffects and optimizing treatment results (<xref ref-type="bibr" rid="B102">Zahin et al., 2020</xref>). In agriculture, nano-enabled precision farming techniques reduce pesticide use while improving nutrient delivery (<xref ref-type="bibr" rid="B40">Goyal et al., 2023</xref>). However, challenges remain in standardization, lifecycle assessment, and responsible scale-up, necessitating continued research and international collaboration. As the world transitions toward circular economies, sustainable nanomaterials are set to play a key role in achieving both technological advancement and environmental preservation (<xref ref-type="bibr" rid="B89">Solomon et al., 2024</xref>).</p>
<p>Increasing attention is given to algae by nanotechnologists, leading to the emergence of a new field called &#x201c;Algae nanotechnology.&#x201d; Because of their special qualities, algae are valued in green nanotechnology and are regarded as green bio-factories of nanoparticles. Usage of algae-mediated nanoparticles in categorized industries includes electronics, textiles, medicine, packaging, food processing, agriculture, food processing, wastewater treatment, and environmental recovery. An algae-based green nanoparticles have potential in environmental remediation in areas such as water treatment, heavy metal remediation, and antimicrobial activities and a sustainable and eco-friendly approach to address environmental pollution by synthesizing nanoparticles from algae (<xref ref-type="bibr" rid="B97">Tonelli et al., 2023</xref>). Extensive research has been conducted on the use of algae for the production of nanobiomaterials and their potential applications in biomedicine (<xref ref-type="bibr" rid="B114">Lewis Oscar et al., 2016</xref>).</p>
<p>Sustainable synthesis of nanomaterial using algae has garnered promising interest in recent times as a safe, straightforward, eco-friendly, economical, and sustainable technique. The most elaborately explored algae for yielding of NPs (Nanoparticles) that have been reported are the red, brown, blue-green, micro, and macro green algae (<xref ref-type="bibr" rid="B24">Chaudhary et al., 2020</xref>). The algal-synthesized nanoparticles have the potential to act as antibacterial agents, antifungal agents, and play their role in targeting specific infections. The sustainable synthesis of algae-mediated nanoparticles highlighted the advantages of this approach, such as eco-friendliness and cost-effectiveness. The antimicrobial and anticancer characteristics of algae-mediated nano-biomaterial emphasized their key role in drug delivery systems and bioimaging (<xref ref-type="bibr" rid="B24">Chaudhary et al., 2020</xref>). The importance of algae-mediated nano-biomaterials in drug delivery and bioimaging is highlighted through their antimicrobial and anticancer properties which allow them to serve as both therapeutic agents and delivery systems. These bioactivities stem from bioactive compounds created by algae as well as from reactive oxygen species which can directly kill microbes and cancer cells while improving the drug load, cellular uptake, and controlled release of the biotherapeutic. Moreover, their biocompatibility, surface modification, and functionalisation promote controlled and sustained release of the therapeutic at the intended diseased site to help with the biodiagnostic imaging. Collectively, these properties position algae nano-biomaterials as versatile systems for theranostic applications. The bio-based mechanisms involved the categorization of nano-biomaterial and various techniques of synthesis. Nanobiomaterials show promising applications across various fields and serve as valuable resources for understanding algae-mediated nanoparticles (<xref ref-type="bibr" rid="B65">Mukherjee et al., 2021</xref>). Algae-mediated synthesis of silver nanoparticles is effective due to their ability to uptake metals and reduce metal ions, and numerous studies have documented different algal species and synthesis methods (<xref ref-type="bibr" rid="B113">Chugh et al., 2021</xref>). Algae play an efficient role in nanotechnology and are vital for many applications in various fields. The biosynthesis and description of nano-biomaterial from different types of algae, such as <italic>Cladophora glomerata</italic> and <italic>Sargassum ilicifolium</italic>, and their potential applications in antifungal activity and absorption control are discussed (<xref ref-type="bibr" rid="B36">El-Sheekh et al., 2022</xref>). A substantial number of studies indicate that nano-biomaterials surpass traditional materials in relation to improving drug solubility and stability, allowing for targeted and controlled release, increasing bioavailability, and reducing overall toxicity, thus addressing the major challenges of conventional drug delivery systems. These advantages have been highlighted in recent papers of nanomaterial-based drug delivery systems and their clinical potential (<xref ref-type="bibr" rid="B98">Veloso and Castanheira, 2023</xref>; <xref ref-type="bibr" rid="B63">Mishra et al., 2024</xref>; <xref ref-type="bibr" rid="B43">Guvvali and Mohanty, 2025</xref>). Furthermore, the potential of nano-biomaterials in biomedical applications, their apoptotic effects and anticancer activity against human colon cancer cells is unravelled (<xref ref-type="bibr" rid="B2">Acharya et al., 2021</xref>). There is an increasing need for new solutions in healthcare due to changes in leading causes of death and the emergence of nosocomial infections and antibiotic resistance. There are possible uses of these nanoparticles as applications in medicines due to their less toxic effect and biocompatibility and the utilization of isolated substances on the surface of the nanoparticles as a means of fighting illness (<xref ref-type="bibr" rid="B86">Sidorowicz et al., 2023</xref>). Micro-algae have received increasing attention from materials scientists due to their versatility and the ease of biosynthesis of valuable nanomaterials. Microalgal strains are used for the production of NPs made of base metals, alloys, oxides, and compounds of chalcogens (<xref ref-type="bibr" rid="B26">Dahoumane et al., 2016</xref>). There are unique advantages of microalgae in nanobiotechnology, including their diversity, physiology, and the versatility of the designed processes. The environmentally friendly synthesis of nano-biomaterial using algae can emphasize the therapeutic potential, particularly in combating bacterial infections.</p>
<p>Green algal nanoparticles have an immense contribution in furthering the United Nations&#x2019; Sustainable Development Goals (SDGs) through challenging the essential ecological as well as social problems. These nanoparticles, sourced from autotrophic organism algae, which are a renewable source of energy, can greatly contribute to different categories of sustainable goals promoted by the United Nations (<xref ref-type="bibr" rid="B112">Hosny et al., 2025</xref>). Green algae-mediated nanoparticles can contribute to SDG 6 (Clean Water and Sanitation) <italic>via</italic> their use in water purification and wastewater treatment. Their unique capability in the elimination of pollutants, heavy elements, and pathogens ensures safer water resources (<xref ref-type="bibr" rid="B75">Rahman et al., 2019</xref>; <xref ref-type="bibr" rid="B65">Mukherjee et al., 2021</xref>). Silver nanoparticles (AgNPs) synthesized from <italic>Chlorella vulgaris</italic> and <italic>Caulerpa racemosa</italic> have demonstrated exceptional antimicrobial properties, effectively eliminating harmful bacteria such as <italic>E. coli</italic> and <italic>Salmonella</italic> from contaminated water (<xref ref-type="bibr" rid="B1">Aboelfetoh et al., 2017</xref>). Green algae-based nanoparticles are employed in pollution reduction by adsorbing and degrading environmental pollutants such as metalloid elements, dyes, and organic pollutants from water and soil (<xref ref-type="bibr" rid="B91">Subramaniyam et al., 2015</xref>; <xref ref-type="bibr" rid="B75">Rahman et al., 2019</xref>). Iron oxide nanoparticles (Fe<sub>3</sub>O<sub>4</sub>) synthesized from <italic>Ulva lactuca</italic> have demonstrated exceptional efficiency in removing toxic metals like lead (Pb) and chromium (Cr) from industrial effluent (<xref ref-type="bibr" rid="B19">Bensy et al., 2022</xref>). By way of integrating these revolutionary materials, a greener and sustainable future can be fostered in multiple sectors (<xref ref-type="bibr" rid="B111">Kumar et al., 2024b</xref>). Green algae-based nanoparticles contribute to SDG 7 (Affordable and Clean Energy) by enhancing biofuel production efficiency and providing a sustainable alternative to fossil fuels. These nanoparticles, derived from renewable algal biomass, act as efficient catalysts in processes such as lipid extraction and transesterification, significantly improving the yield of biodiesel and bioethanol (<xref ref-type="bibr" rid="B60">Mata et al., 2010</xref>). Nanoparticles synthesized from <italic>C. vulgaris</italic> and <italic>Spirulina platensis</italic> have been shown to optimize bioenergy production by increasing the transformation rates of algal lipids to usable fuels (<xref ref-type="bibr" rid="B83">Shahid et al., 2020</xref>). In agriculture, green algal nanoparticles can improve crop yield as well as soil health, supporting SDG 2 (Zero Hunger). Zinc oxide nanoparticles (ZnO NPs) synthesized from <italic>Tetraselmis indica</italic> and <italic>Spirogyra hyalina</italic> have been shown to improve seed emergence, root development, and overall biomass, leading to increased agricultural output (<xref ref-type="bibr" rid="B20">Bhakya et al., 2016</xref>; <xref ref-type="bibr" rid="B44">Hameed et al., 2023</xref>). Additionally, green algal nanoparticles contribute to soil health by enhancing microbial activity and nutrient availability, reducing the need for synthetic fertilizers and lessening environmental pollution. By improving agricultural productivity and sustainability, these nanoparticles help ensure food security, particularly in regions facing food shortages, thus addressing global hunger challenges. Furthermore, their fairly wide-ranging role, within carbon sequestration and in pollution reduction, substantially aids in combating climate change, directly contributing towards SDG 13 (Climate Action). Green algae, known for their high photosynthetic efficiency, naturally capture and store carbon dioxide (CO<sub>2</sub>) from the atmosphere, and this capability is further enhanced when combined with nanotechnology (<xref ref-type="bibr" rid="B60">Mata et al., 2010</xref>; <xref ref-type="bibr" rid="B67">Olabi et al., 2023</xref>). Nanoparticles derived from <italic>C. vulgaris</italic> and <italic>Spirulina platensis</italic> have been used to optimize CO<sub>2</sub> fixation during algal cultivation, increasing biomass production while reducing greenhouse gas emissions.</p>
<sec id="s1-1">
<label>1.1</label>
<title>Novelty of the review</title>
<p>This review presents a comprehensive and critical analysis of green algae-based NPs and their cutting-edge applications in advancing SDGs. While previous reviews have explored algal biotechnology or green synthesis of NPs, this work uniquely integrates these domains by focusing on how algae-derived NPs address key sustainability challenges such as clean energy, environmental remediation, and healthcare while aligning with specific SDG targets. The novelty lies in a systematic evaluation of algae-mediated NP synthesis mechanisms, emphasizing their eco-friendly advantages over conventional methods, forward-looking discussion on the role of algal NPs in cross-disciplinary SDG applications and identifying underexplored synergies between algal nanotechnology and circular bioeconomy principles. By bridging gaps between nanotechnology, sustainability science, and algal research, this review offers a timely roadmap for harnessing algae-based NPs as transformative tools for global sustainable development.</p>
</sec>
<sec id="s1-2">
<label>1.2</label>
<title>Rationale behind the work</title>
<p>The rising demand for sustainable nanomaterials necessitates alternatives to laboratory-grown synthetic nanoparticles, which often involve toxic reagents and energy-intensive processes. Green algae, with their rapid growth, carbon sequestration potential, and metal-accumulating properties, provide an ideal platform for eco-friendly NP synthesis. This review is motivated by the urgent need to align emerging biogenic nanomaterials with the SDG framework, offering scalable solutions to environmental and societal challenges while minimizing ecological footprints.</p>
</sec>
</sec>
<sec id="s2">
<label>2</label>
<title>Green algae as a source for nanomaterials</title>
<p>The biological composition of green algae, including alkaloids, phenols, flavonoids, carbohydrates, proteins, and pigments like chlorophyll and carotenoids, plays a central role in the eco-friendly synthesis of NPs by serving as natural reducing, capping, and stabilizing agents (<xref ref-type="bibr" rid="B65">Mukherjee et al., 2021</xref>). Phenolic compounds and flavonoids donate electrons to reduce metal ions (e.g., Ag<sup>&#x2b;</sup> &#x2192; Ag<sup>0</sup>) while preventing aggregation, enabling the composite of stable nanoparticles with restricted dimensions (5&#x2013;50&#xa0;nm) and morphology (<xref ref-type="bibr" rid="B94">Sysak et al., 2023</xref>). Carbohydrates (e.g., algal polysaccharides) and proteins further functionalize nanoparticles, enhancing biocompatibility for biomedical applications like drug delivery and antimicrobial coatings (<xref ref-type="bibr" rid="B104">Zhang et al., 2022</xref>). This biomolecular diversity not only eliminates the need for toxic chemical reagents but also imparts unique biological activities (e.g., antioxidant, anticancer) to the nanoparticles, making algal-mediated synthesis a sustainable and multifunctional approach.</p>
<p>The potential of nanoparticles copied from green algae focuses on their synthesis, characterization, and applications in achieving sustainability targets. Green algae such as <italic>Chlorella</italic> and <italic>Scenedesmus</italic> offer significant potential for nanoparticle production due to their rapid growth, high biomass yield, and minimal environmental impact. These algae-mediated nanoparticles exhibit unique physicochemical features, including large surface area and biocompatibility, which enhance their effectiveness in a range of applications. In agriculture, they improved soil productivity and promoted plant proliferation, decreasing the use of synthetic fertilizers. Additionally, their role in energy sector advancements is noted, particularly in the progression of potent solar cells and as catalysts in biofuel production. Furthermore, the biocompatibility and non-toxicity of algae-based nanoparticles support their use in biomedical sciences, like pharmaceutical delivery and imaging, which aligns with health-related SDGs. Green synthesis process also supports economic and environmental goals by minimizing hazardous waste and reducing the carbon footprint associated with conventional nanoparticle production methods (<xref ref-type="bibr" rid="B58">Makarevi&#x10d;ien&#x117; et al., 2011</xref>; <xref ref-type="bibr" rid="B84">Sharma et al., 2020</xref>).</p>
<p>Green algae present a viable answer to environmental problems and can be used to considerably promote sustainable development. Due to their ability to develop quickly and have a high photosynthetic efficiency, green algae may be grown in a variety of settings, such as saltwater and wastewater, which lessens the demand on conventional agricultural resources (<xref ref-type="bibr" rid="B68">Oliveira et al., 2022</xref>). Their vital function in absorbing carbon dioxide aids in decreasing greenhouse gas discharge to combat climate change. Green algae can also be used to produce biofuel, which is another renewable energy source that reduces dependency on fossil fuels. Their capacity to yield beneficial by-products like fertilizers and bioactive chemicals increases their potential for sustainable farming methods (<xref ref-type="bibr" rid="B9">Alvarenga et al., 2023</xref>). Green algae can help us create a more resilient and sustainable future that meets both ecological and economic demands by being incorporated into development initiatives (<xref ref-type="bibr" rid="B67">Olabi et al., 2023</xref>).</p>
<sec id="s2-1">
<label>2.1</label>
<title>Synthesis of nano-biomaterial using green algae</title>
<p>Green algae are of two primary groups: microscopic and larger green algae, adapted to their surroundings. Microscopic green algae are primarily grown in freshwater environments and are unicellular in nature, while macro green algae are multicellular marine plant-like organisms (<xref ref-type="bibr" rid="B28">Deglint et al., 2019</xref>). It is currently common practice to biosynthesize several metal oxides, bimetallic, and monometallic nanoparticles (NPs) from green algae. As of now, about 20 different classes of microgreen algae are used in the production of AgNPs. <italic>Pithophoraoedogonia, Chlorococcumhumicola, C. vulgaris, C. reinhardtii,</italic> and <italic>Enteromorpha flexuosa</italic> produce extracellular AgNPs with different geometrical features (<xref ref-type="bibr" rid="B47">Jena et al., 2014</xref>; <xref ref-type="bibr" rid="B101">Yousefzadi et al., 2014</xref>). Several strains of green macroalgae have been completely utilized in the manufacturing of metallic nanoparticles recently. Thebeneficial green macroalgae species, <italic>Ulva fasciata</italic>, was utilized to generate nano-scale silver colloids. The antibacterial qualities of these colloids were then assessed by adapting them to cotton fabric (<xref ref-type="bibr" rid="B57">Madhiyazhagan et al., 2017</xref>). There are several industrial, medical, and biotechnological uses for micro green algae, being a member of the Cladophorales order. Numerous important components, including alkaloids, phenols, flavonoids, carbohydrates, and functional groups, are abundant in them and may function as both alleviating and reducing agents around the micro-mediated production of nanoparticles (<xref ref-type="bibr" rid="B101">Yousefzadi et al., 2014</xref>). <xref ref-type="table" rid="T1">Table 1</xref> describes the algal-mediated synthesis of metal nanoparticles using different reagents, highlighting the algal species employed, type of algae, metal precursors, bio-reducing/capping biomolecules, and their associated applications, along with recent literature references.</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Algal-mediated synthesis of metal nanoparticles using different reagent.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Algal species</th>
<th align="left">Nanoparticle type</th>
<th align="left">Metal precursor</th>
<th align="left">Bio-reducing/capping biomolecules</th>
<th align="left">Key aspect of nanoparticles</th>
<th align="left">References</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">
<italic>Galaxaura rugosa</italic>
</td>
<td align="left">Ag&#x2013;Fe bimetallic NPs</td>
<td align="left">AgNO<sub>3</sub>, Fe<sup>3&#x2b;</sup> salts</td>
<td align="left">Polyphenols, proteins, polysaccharides</td>
<td align="left">Green synthesis of multifunctional bimetallic NPs with environmental and biomedical relevance</td>
<td align="left">
<xref ref-type="bibr" rid="B66">Nosrati et al. (2025)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Laurencia papillosa</italic>
</td>
<td align="left">AgNPs</td>
<td align="left">AgNO<sub>3</sub>
</td>
<td align="left">Phenolics, proteins, sulfated polysaccharides</td>
<td align="left">Antimicrobial activity and environmental remediation</td>
<td align="left">
<xref ref-type="bibr" rid="B32">El Shehawy et al. (2023)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Caulerpa sertularioides</italic>
</td>
<td align="left">AgNPs</td>
<td align="left">Ag<sup>&#x2b;</sup> precursor</td>
<td align="left">Proteins, polysaccharides, phenolic compounds</td>
<td align="left">Antioxidant and antibacterial properties</td>
<td align="left">
<xref ref-type="bibr" rid="B10">Anjali et al. (2022)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Ulva</italic> spp.</td>
<td align="left">ZnO NPs</td>
<td align="left">Zn(NO<sub>3</sub>)<sub>2</sub>/Zn<sup>2&#x2b;</sup> salts</td>
<td align="left">Polysaccharides, hydroxyl-rich biomolecules</td>
<td align="left">Photocatalysis, antibacterial activity</td>
<td align="left">
<xref ref-type="bibr" rid="B56">L&#xf3;pez-Miranda et al. (2023)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Synechococcus moorigangae</italic>
</td>
<td align="left">AuNPs</td>
<td align="left">HAuCl<sub>4</sub>
</td>
<td align="left">Proteins, pigments, extracellular polymers</td>
<td align="left">Antioxidant and antimicrobial applications</td>
<td align="left">(Rosyidah et al., 2024)</td>
</tr>
<tr>
<td align="left">
<italic>Padina tetrastromatica</italic>
</td>
<td align="left">AuNPs</td>
<td align="left">HAuCl<sub>4</sub>
</td>
<td align="left">Polyphenols, flavonoids, terpenoids</td>
<td align="left">Catalytic dye degradation; size-controlled AuNPs</td>
<td align="left">
<xref ref-type="bibr" rid="B72">Princy and Gopinath (2018)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Turbinaria conoides</italic>
</td>
<td align="left">AuNPs</td>
<td align="left">AuCl<sub>4</sub>
<sup>&#x2212;</sup>
</td>
<td align="left">Polyphenols, polysaccharides</td>
<td align="left">Rapid green synthesis of small, stable AuNPs</td>
<td align="left">
<xref ref-type="bibr" rid="B77">Rajeshkumar et al. (2013)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Sargassum subrepandum</italic>
</td>
<td align="left">AgNPs</td>
<td align="left">AgNO<sub>3</sub>
</td>
<td align="left">Fucoidan, phenolics, proteins</td>
<td align="left">Antimicrobial, anticancer, and molluscicidal activities</td>
<td align="left">
<xref ref-type="bibr" rid="B34">El-Sayed et al. (2024)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Sargassum polycystum</italic>
</td>
<td align="left">AgNPs</td>
<td align="left">AgNO<sub>3</sub>
</td>
<td align="left">Brown algal polyphenols and proteins</td>
<td align="left">Biomedical screening and biological activity</td>
<td align="left">
<xref ref-type="bibr" rid="B96">Thiurunavukkarau et al. (2022)</xref>
</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>A diagrammatic representationof the biosynthesis of Ag NPs by <italic>Shyalina</italic> has been given in <xref ref-type="fig" rid="F1">Figure 1</xref>.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>The flow chart shows steps in silver nanoparticle synthesis: <bold>(A)</bold> Gathering <italic>Shyalina</italic> from a local pond, <bold>(B)</bold> Shade drying, <bold>(C)</bold> Powdering the algae, <bold>(D)</bold> <italic>Shyalina</italic> extract, <bold>(E)</bold> silver nitrate, and <bold>(F)</bold> 1&#xa0;mM silver nitrate solution <bold>(G)</bold> Adding <italic>Shyalina</italic> extract to silver nitrate solution, <bold>(H)</bold> Placing the mixture on a magnetic stirrer to facilitate the reaction <bold>(I)</bold> Centrifugation, to separate the nanoparticles from the reaction mixture. <bold>(J)</bold> Pure silver NPs are collected and <bold>(K)</bold> The reaction of silver nitrate with the algal extract results in the formation of silver nanoparticles. Reproduced from (<xref ref-type="bibr" rid="B5">Al-Radadi et al., 2022</xref>), under the CC BY-NC-ND 4.0 license.</p>
</caption>
<graphic xlink:href="fnano-08-1751841-g001.tif">
<alt-text content-type="machine-generated">Step-by-step process of synthesizing silver nanoparticles using *Spirogyra hyalina*. Images A to J show preparation stages including drying, grinding, extraction, heating, and centrifugation. Diagram K illustrates the molecular interaction between silver ions (Ag+) and biomolecules from the extract, leading to nanoparticle formation.</alt-text>
</graphic>
</fig>
<p>Morphological features and size distribution are crucial parameters for studying bio-synthesized nanoparticles and their applications. The scanning electron microscope reveals the topographyof spirulina-mediated TiO<sub>2</sub> nanoparticles, which are circular in shape with an average particle size of 55 &#xb1; 15&#xa0;nm, as shown in <xref ref-type="fig" rid="F2">Figure 2</xref>.</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>
<bold>(a)</bold> Morphological analysis of TiO<sub>2</sub> nanoparticles biosynthesized by <italic>Spirulina</italic> with a scanning electron microscope with a scaling bar at 0.5&#xa0;&#x3bc;m. <bold>(b)</bold> Morphological analysis of TiO<sub>2</sub> nanoparticles biosynthesized by <italic>Spirulina</italic> with a scanning electron microscope with a scaling bar at 100&#xa0;nm. <bold>(c)</bold> EDX analysis of the elemental composition of the <italic>Spirulina</italic> mediated TiO<sub>2</sub> nanoparticles. Reproduced with permission from (<xref ref-type="bibr" rid="B61">Mathesh et al., 2024</xref>), &#xa9; Elsevier 2024.</p>
</caption>
<graphic xlink:href="fnano-08-1751841-g002.tif">
<alt-text content-type="machine-generated">Scanning electron microscope images with two panels: (a) shows a higher magnification view of a porous structure composed of clustered particles; (b) depicts the same material at a lower magnification, showing slightly larger agglomerates. Below, a spectrum graph displays elemental analysis with peaks for elements labeled, indicating material composition.</alt-text>
</graphic>
</fig>
</sec>
</sec>
<sec id="s3">
<label>3</label>
<title>Mechanisms engaging in the synthesis of algae-derived NPs</title>
<p>Several microalgal metabolite processes that can convert metal cation sources into a zerovalent state are crucial to the formation of nanoparticles. Using physical or chemical methods, the top-down strategy attempts to breakdown bulk materials into nano-range particles (<xref ref-type="bibr" rid="B45">Hamida et al., 2020</xref>). In addition to being energy-intensive and generating hazardous and biohazardous materials, algae-derived nanoparticle synthesis is costly and risky due to the need for controlled cultivation conditions, low and variable yields, complex downstream purification processes, susceptibility to biological contamination, and challenges in standardization and regulatory compliance. Some common reagents like sodium borohydride (NaBH<sub>4</sub>), hydrazine and Cetyltrimethylammonium bromide are toxic and hazardous, producing reactive by-products and requiring careful handling. The only possible variation in the generated nanoparticles&#x2019; size is not in their characteristics. The bottom-up method, which uses chemical and biological techniques to change atoms or ions into their stable form at the nanoscale, is incredibly effective (<xref ref-type="bibr" rid="B35">El-sheekh et al., 2021</xref>). The mechanism for algal manufacture of nanoparticles begins with binding, accumulation, reduction at inter intercellular level, and ends with creation at the outer cellular level (<xref ref-type="bibr" rid="B51">Khanna et al., 2019</xref>). The process of reduction is influenced by certain living and non-living components. The fatty acids in the plasma membrane, the reducing sugars in the polysaccharide sheath, and other cellular reducing entities are examples of abiotic factors. According to (<xref ref-type="bibr" rid="B15">Bakir et al., 2018</xref>), reducing enzymes is one of the biotic factors. Biosynthesis of green algae involves two mechanisms i.e., Intracellular and Extracellular.</p>
<p>
<xref ref-type="fig" rid="F3">Figure 3</xref> illustrates various pathways implemented in the algae for the synthesis of NPs. Initially, metal ions (M<sup>&#x2b;</sup>) in a salt solution are either adsorbed onto the cell walls of the algae or taken up by the biomass. M<sup>&#x2b;</sup> interactions are facilitated by extracellular enzymes and proteins from the algae, as well as functional groups from the algae cell membrane which start the biosorption and reduction. Biomolecules such as polysaccharides, proteins, organic acids, and the redox cofactor (NAD/NAD<sup>&#x2b;</sup>) are present within and outside of the algal cells and serve as M<sup>&#x2b;</sup> reducing agents. During the process of photosynthesis, further electrons are supplied by the photosynthetic pigments (chlorophyll a and b) which aid in M<sup>&#x2b;</sup> reduction. The algal cell surrounding the metal nanoparticles, adsorbing the algal cell walls, and reducing M<sup>&#x2b;</sup> to metal nanoparticles (M<sup>0</sup>), and reduces M<sup>&#x2b;</sup>, and adds (NAD<sup>&#x2b;</sup>) to M<sup>0</sup>, are engulfed by the algae and, and adds (NAD<sup>&#x2b;</sup>) to M<sup>0</sup>, and adds cofactor. Conclusively, the algae illustrates the role of biosorption (M<sup>&#x2b;</sup>) and reduction (M<sup>0</sup>) as well as stabilizing ball in the green metal synthesis of nanoparticles.</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>Algae-mediated nanoparticles synthesis pathway.</p>
</caption>
<graphic xlink:href="fnano-08-1751841-g003.tif">
<alt-text content-type="machine-generated">Diagram illustrating the process of nanoparticle synthesis using green algae. Metal salt solution is taken up by biomass. The extracellular enzymes and proteins, along with chlorophyll pigments, lead to photosynthesis. This results in oxidation and reduction processes, forming stabilized nanoparticles via capping. Components include extracellular membrane, carbohydrates, proteins, organic acids, and NAD/NAD+ cycles.</alt-text>
</graphic>
</fig>
<sec id="s3-1">
<label>3.1</label>
<title>Intracellular nanoparticles formation by green algae</title>
<p>By incubating <italic>Ulva intestinalis</italic> and <italic>Rhizoclonium fontinale</italic> algae in chloroauric acid for 72&#xa0;h at 20&#xa0;&#xb0;C, AuNPs are produced intracellularly. The biosynthesis of AuNPs is indicated by a discernible purple colour shift of the thallus from green. Colour alteration could not be observed when the gold metal solution was developed with biological material, proving that no metabolites or intracellular enzymes were connected to the bio-reduction process. Among the most beneficial green seaweed species, <italic>Ulva fasciata</italic> was accustomed to produce nano-sized silver colloids, which were then applied to cotton fabric with and without citric acid to test their antimicrobial effectiveness (<xref ref-type="bibr" rid="B33">El-Rafie et al., 2013</xref>). In an alternative experiment, the silica gel suspension that contained <italic>Klebsormidium flaccidum</italic> demonstrated a visible purple colour shift in the chloroplast from green, indicating the ability of the cells to reduce the gold precursor (chloroauric acid). The existence of reduced gold precursor salt by the NADPH-dependent reductase enzyme or NADPH was furthersubstantiated by TEM investigation, that revealed dark-coloured patches within the thylakoid membrane (<xref ref-type="bibr" rid="B85">Sicard et al., 2010</xref>). Similarly, the algal cell wall of <italic>Tetraselmiskochinensis</italic>was shown to synthesize AuNPs intracellularly. The non-existence of the creation of substances outside the cell was unequivocally confirmed by UV-visible spectroscopy. The cytoplasmic region did not contain as many AuNPs as the vicinity of the cell wall, which is apparently due to bioactive moieties that cause bio-reduction (<xref ref-type="bibr" rid="B82">Senapati et al., 2012</xref>).</p>
</sec>
<sec id="s3-2">
<label>3.2</label>
<title>Extracellular nanoparticles formation by green algae</title>
<p>Various methods, including supernatant-based non-cell culture medium and cell organic material extracts, can be employed for the outside cell production of nanobiomaterials by algae. A vast majority of micro green algae species, including <italic>Pithophora oedogonia</italic> (cuboid and hexangular, 24&#x2013;55&#xa0;nm), <italic>Chlorococcum humicola</italic> (globular, 16&#xa0;nm), <italic>Chlorella vulgaris</italic> (trilateral, 28&#xa0;nm), <italic>C. reinhardtii</italic> (quadrate and ring, 1&#x2013;15&#xa0;nm), and <italic>Enteromorpha flexuosa</italic> (disc-shaped, 15&#xa0;nm), are used to generate AgNPs extracellularly (<xref ref-type="bibr" rid="B100">Xie et al., 2007</xref>; <xref ref-type="bibr" rid="B17">Barwal et al., 2011</xref>; <xref ref-type="bibr" rid="B47">Jena et al., 2014</xref>; <xref ref-type="bibr" rid="B101">Yousefzadi et al., 2014</xref>). Much research has been done recently on the green microalgae-mediated production of AuNPs, which is similar to AgNPs, as shown in <xref ref-type="table" rid="T2">Table 2</xref>. One of the most extensively used species of microalgae, <italic>Pithophora crispa</italic> from higher altitudes, reduces the precursor salt of chloroauric acid to produce AuNPs through the assistance of extracellular and intracellular proteins and peptides (<xref ref-type="bibr" rid="B100">Xie et al., 2007</xref>). Another significant species of kelp, <italic>Chaetomorpha linum</italic>, is known for its environment-derived function in controlling the availability of food components in its dwelling space. AgNPsare synthesized by prompting the reduction of silver ions (Ag<sup>&#x2b;</sup>) to Ag<sup>0</sup> in the extracellular environment with the aid of peptides, flavonoids, and terpenoids (<xref ref-type="bibr" rid="B73">Priyadharshini et al., 2014</xref>). In addition to AgNPs, green macroalgal species, including <italic>R. fontinale</italic> and <italic>Prasiola crispa</italic> have also been known to synthesize AuNPs. Due to their application in targeted medication delivery for cancer treatment, AuNPs have gained prominence lately. The synthesis of AuNPs is always difficult because of their irreproducibility at the perfect dimension and form; however, green macroscopic algae overcame this difficulty and produced constant and repeatable AuNPs (<xref ref-type="bibr" rid="B55">Lakshmi et al., 2012</xref>; <xref ref-type="bibr" rid="B70">Parial and Pal, 2014</xref>; <xref ref-type="bibr" rid="B73">Priyadharshini et al., 2014</xref>).</p>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>The lists of green algae-mediated biosynthesis of nanoparticles.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Algae</th>
<th align="center">NPs</th>
<th align="center">Location</th>
<th align="center">Shape and size</th>
<th align="center">Application</th>
<th align="center">References</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">
<italic>Acutodesmusdimorphus</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">Sph, 2&#x2013;20&#xa0;nm</td>
<td align="left">Antioxidant</td>
<td align="left">
<xref ref-type="bibr" rid="B65">Mukherjee et al. (2021)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Botryococcusbraunii</italic>
</td>
<td align="left">Ag, Pd, Pt</td>
<td align="left">Extracellular</td>
<td align="left">Sph, 16&#xa0;nm</td>
<td align="left">Bactericidal, Antifungal, Antioxidant</td>
<td align="left">
<xref ref-type="bibr" rid="B12">Arya et al. (2019)</xref>, <xref ref-type="bibr" rid="B13">2020</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Caulerpa racemose</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">Sph, Tri, 5&#x2013;25&#xa0;nm</td>
<td align="left">Bactericidal</td>
<td align="left">
<xref ref-type="bibr" rid="B50">Kathiraven et al. (2015)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Caulerpa serrulata</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">Rob, Col-shaped</td>
<td align="left">Antibacterial</td>
<td align="left">
<xref ref-type="bibr" rid="B1">Aboelfetoh et al. (2017)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Chaetomorpha linum</italic>
</td>
<td align="left">Ag, Au</td>
<td align="left">Extracellular</td>
<td align="left">Coal, 3&#x2013;44&#xa0;nm</td>
<td align="left">Anti-Cancerous activity</td>
<td align="left">
<xref ref-type="bibr" rid="B49">Kannan et al. (2013)</xref>, <xref ref-type="bibr" rid="B2">Acharya et al. (2021)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Chlamydomonas reinhardtii</italic>
</td>
<td align="left">Ag, CuO</td>
<td align="left">Extracellular</td>
<td align="left">Rec,Rou, 1&#x2013;15&#xa0;nm</td>
<td align="left">Antioxidant</td>
<td align="left">
<xref ref-type="bibr" rid="B17">Barwal et al. (2011)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Chlorella minutissima</italic>
</td>
<td align="left">Ag</td>
<td align="left">&#x200b;</td>
<td align="left">Sph&#x223c;14.65 &#xb1; 3.95</td>
<td align="left">Antibacterial, Anti-oxidant and catalytic</td>
<td align="left">
<xref ref-type="bibr" rid="B103">Zayadi and Abu Bakar (2020)</xref>, <xref ref-type="bibr" rid="B54">Kumar et al. (2024a)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Chlorella pyrenoidosa</italic>
</td>
<td align="left">TiO, Au</td>
<td align="left">Extracellular</td>
<td align="left">FCC, 5&#x2013;20&#xa0;nm, Ico, Sph, 25&#x2013;30&#xa0;nm</td>
<td align="left">Bactericidal photocatalytic</td>
<td align="left">
<xref ref-type="bibr" rid="B14">Aziz et al. (2015)</xref>, <xref ref-type="bibr" rid="B62">Middepogu et al. (2018)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Chlorella vulgaris</italic>
</td>
<td align="left">Ag, Au, Si, Fe<sub>3</sub>O<sub>4</sub>, Pd</td>
<td align="left">Extracellular</td>
<td align="left">Tri, 28&#xa0;nm</td>
<td align="left">Bactericidal</td>
<td align="left">
<xref ref-type="bibr" rid="B11">Arsiya et al. (2017)</xref>, <xref ref-type="bibr" rid="B105">Z&#xfa;&#xf1;iga-Miranda et al. (2023)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Chlorococcumhumicola</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">Sph, 4 and 6&#xa0;nm</td>
<td align="left">Bactericidal</td>
<td align="left">
<xref ref-type="bibr" rid="B48">Jenaa et al. (2013)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Codium capitatum</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">3&#x2013;44&#xa0;nm</td>
<td align="left">&#xa0;Anticancer</td>
<td align="left">
<xref ref-type="bibr" rid="B73">Priyadharshini et al. (2014)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Coelastrella</italic> sp.</td>
<td align="left">Au</td>
<td align="left">Intracellular</td>
<td align="left">Sph, 30&#xa0;nm</td>
<td align="left">Antioxidant</td>
<td align="left">
<xref ref-type="bibr" rid="B64">MubarakAli et al. (2013)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Enteromorpha compressa</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">Sph, 0&#x2013;50&#xa0;nm</td>
<td align="left">Biomedical and agriculture applications</td>
<td align="left">
<xref ref-type="bibr" rid="B49">Kannan et al. (2013)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Enteromorpha flexuosa</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">Cir, 15&#xa0;nm</td>
<td align="left">Antimicrobial</td>
<td align="left">
<xref ref-type="bibr" rid="B101">Yousefzadi et al. (2014)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Klebsormidiumflaccidum</italic>
</td>
<td align="left">Au</td>
<td align="left">Intracellular</td>
<td align="left">10&#x2013;20&#xa0;nm</td>
<td align="left">&#xa0;Photosynthesis-based cellular biosensors</td>
<td align="left">
<xref ref-type="bibr" rid="B85">Sicard et al. (2010)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Neodesmuspupukensis</italic>
</td>
<td align="left">Ag, Au</td>
<td align="left">-</td>
<td align="left">-</td>
<td align="left">Antioxidant, Antibacterial, Antifungal</td>
<td align="left">
<xref ref-type="bibr" rid="B69">Omomowo et al. (2020)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Pithophoraoedogonia</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">Cub, Hex, 25&#x2013;44&#xa0;nm</td>
<td align="left">Antibacterial</td>
<td align="left">
<xref ref-type="bibr" rid="B87">Sinha et al. (2015)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Spirogyra hyalina</italic>
</td>
<td align="left">ZnO, Fe<sub>3</sub>O<sub>4</sub>
</td>
<td align="left">-</td>
<td align="left">Sph, 52&#xa0;nm</td>
<td align="left">Antioxidant, Antibacterial</td>
<td align="left">
<xref ref-type="bibr" rid="B44">Hameed et al. (2023)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Spirogyra varians</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">FCC, 17.6&#xa0;nm</td>
<td align="left">Antibacterial</td>
<td align="left">
<xref ref-type="bibr" rid="B80">Salari et al. (2016)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Tetraselmis indica</italic>
</td>
<td align="left">ZnO</td>
<td align="left">-</td>
<td align="left">-</td>
<td align="left">Antioxidant, Antibacterial, Hemolytic Activity</td>
<td align="left">
<xref ref-type="bibr" rid="B20">Bhakya et al. (2016)</xref>, <xref ref-type="bibr" rid="B95">Thirumoorthy et al. (2021)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Tetraselmiskochinensis</italic>
</td>
<td align="left">Au</td>
<td align="left">Intracellular</td>
<td align="left">Tri, FCC, Sph, 5&#x2013;35&#xa0;nm</td>
<td align="left">Drugdelivery</td>
<td align="left">
<xref ref-type="bibr" rid="B82">Senapati et al. (2012)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Ulva conglobata</italic>
</td>
<td align="left">Ag</td>
<td align="left">&#x200b;</td>
<td align="left">Sph, 25&#x2013;40&#xa0;nm</td>
<td align="left">Bactericidal</td>
<td align="left">
<xref ref-type="bibr" rid="B88">Solanki et al. (2023)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Ulva fasciata</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">Sph, 28&#x2013;41&#xa0;nm</td>
<td align="left">Bactericidal</td>
<td align="left">
<xref ref-type="bibr" rid="B38">Fouda et al. (2022)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Ulva flexousa</italic>
</td>
<td align="left">Ag</td>
<td align="left">Extracellular</td>
<td align="left">Cir and FCC, 2&#x2013;32&#xa0;nm</td>
<td align="left">Bactericidal and Antifungal</td>
<td align="left">
<xref ref-type="bibr" rid="B74">Rahimi et al. (2014)</xref>, <xref ref-type="bibr" rid="B59">Mashjoor et al. (2018)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Ulva intestinalis</italic>
</td>
<td align="left">Ag, Au</td>
<td align="left">Extracellular</td>
<td align="left">-</td>
<td align="left">Vaccine development</td>
<td align="left">
<xref ref-type="bibr" rid="B39">Gonz&#xe1;lez-Ballesteros et al. (2019)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Ulva lactuca</italic>
</td>
<td align="left">Ag, Au</td>
<td align="left">-</td>
<td align="left">Sph, 25&#x2013;40&#xa0;nm</td>
<td align="left">Bactericidal, Antifungal</td>
<td align="left">
<xref ref-type="bibr" rid="B21">Bhimba and Kumari (2014)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Urospora</italic> sp.</td>
<td align="left">Ag, Si</td>
<td align="left">Extracellular</td>
<td align="left">FCC, Sph, 20&#x2013;30&#xa0;nm</td>
<td align="left">Antibacterial</td>
<td align="left">
<xref ref-type="bibr" rid="B93">Suriya et al. (2012)</xref>
</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
</sec>
<sec id="s4">
<label>4</label>
<title>Application of green algae-mediated NPs</title>
<p>The nanoparticles&#x2019; distinctive qualities include heat conduction, optical and magnetic polarizability, biocompatibility, and catalytic efficiency. They can also permeatebiomolecules like DNA and proteins as a result of their minuscule size. To use them in various applications, this encourages enhancing their features (<xref ref-type="bibr" rid="B42">Guruviah et al., 2019</xref>). Nano-biomaterials have attracted considerable attention in the healthcare and biotech fields. Their applications encompass drug and gene delivery, tissue engineering, tumor eradication, cancer therapy, antimicrobial agents, anticoagulant separation techniques, DNA analysis, biosensing, catalytic processes, and enhanced magnetic resonance imaging (MRI) contrast (<xref ref-type="bibr" rid="B16">Barabadi et al., 2017</xref>; <xref ref-type="bibr" rid="B51">Khanna et al., 2019</xref>). Ag-NPs and Au-NPs were used to enhance the healing and recovery processes of surgical orthopaedic prostheses, bandages, contraceptive devices, surgical mesh, and equipment. Ag-NPs, which are combined with silver sulfadiazine and applied as pastes to treat burns, toxic epidermal necrolysis, and different types of ulcers. Nanoparticles have enhanced various biotechnological applications including food packaging, the food industry, water purification, laundry machines and textiles by inhibiting bacterial growth and preventing the formation of slime biofilms (<xref ref-type="bibr" rid="B110">Panda et al., 2020</xref>). The current research status and prospects of algal nanoparticles showcase the antibacterial activity and cytotoxicity (<xref ref-type="bibr" rid="B18">Behera et al., 2023</xref>). The green synthesis methods, particularly using seaweed extracts, can be used to produce zinc oxide nanoparticles (ZnONPs). The efficient reduction of zinc ions by algae extracts leads to the formation of pure ZnONPs with antibacterial and photocatalytic properties was discovered and the characterization techniques are employed, including SEM, XRD, and FTIR, to confirm the nanoparticle formation (<xref ref-type="bibr" rid="B7">Alprol et al., 2023</xref>).</p>
<sec id="s4-1">
<label>4.1</label>
<title>Antioxidant</title>
<p>
<italic>Tetraselmis indica</italic> extract creates ZnO nanoparticles during the reduction of zinc acetate using a green synthesis technique. The DPPH free radical scavenging assay was used to inquire the zinc oxide nanoparticles&#x2019; antioxidant capacity. Acquiring hydrogen or electrons from the donor atom, which are then taken up by the odd electron of DPPH and change into identical hydrazine, reduces the free radical of 1-diphenyl-2-picrylane (<xref ref-type="bibr" rid="B20">Bhakya et al., 2016</xref>). The absorbance at 517&#xa0;nm is used to quantify the observed decline of the colour faded from purple to yellow. When compared to ascorbic acid, the zinc nanoparticles&#x2019; free radical scavenging activity was nearly alike. The concentration of 100&#xa0;mg mL&#x2212;1 showed the greatest percentage of inhibition, indicating an 87.31% reduction, and this was higher than the concentrations of 75&#xa0;mg mL&#x2212;1%&#x2013;77.62% and 50&#xa0;mg mL&#x2212;1%&#x2013;65.35%. The green ZnO NP that was produced from <italic>Tetraselmis indica</italic> was an effective scavenger of hydroxyl radicals. One significant antioxidant component in ZnO was phenol (<xref ref-type="bibr" rid="B95">Thirumoorthy et al., 2021</xref>). The synthesized UL-ZrO<sub>2</sub>NPs using the <italic>Ulva lactuca</italic> extract were assessed for antioxidant activity, and the results were profoundly efficient. The activity was measured using the DPPH method with standard ascorbic acid. In comparison to traditional ascorbic acid, UL-ZrO<sub>2</sub>NPs demonstrated a little lower antioxidant activity as illustrated in <xref ref-type="fig" rid="F4">Figure 4</xref>.</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>
<bold>(a)</bold> DPPH radical inhibition activity; <bold>(b)</bold> Hydroxyl scavenging activity of UL-ZrO<sub>2</sub>NPs from <italic>Ulva lactuca</italic>. Reproduced with permission from (<xref ref-type="bibr" rid="B92">Sudhakar et al., 2025</xref>), &#xa9; Elsevier 2025.</p>
</caption>
<graphic xlink:href="fnano-08-1751841-g004.tif">
<alt-text content-type="machine-generated">Bar graphs labeled (a) and (b) compare the inhibition percentages at different concentrations of ascorbic acid and UL-ZrO&#x2082; nanoparticles. The x-axis represents concentration in micrograms per milliliter, while the y-axis shows inhibition percentage. Both graphs use orange bars for ascorbic acid and green for UL-ZrO&#x2082; nanoparticles. Graph (a) shows increasing inhibition for both substances, while graph (b) shows a consistent pattern across concentrations of 50 to 250 micrograms per milliliter.</alt-text>
</graphic>
</fig>
<p>Utilizing the DPPH (2,2-diphenyl-2-picrylhydrazyl hydrate) test, the antioxidant plausible of both AgNPs and AuNPs was synthesized from cell-free extract of <italic>Neodesmuspupukensis</italic>. To dissolve 1.97&#xa0;g of DPPH, 5&#xa0;mL of methanol was used. Three millilitres of hydrogel solution, 1&#xa0;mL of prepared hydrogel in 10&#xa0;mL of distilled water, were combined with 1&#xa0;mL of this solution. The concoction was agitated and kept at rest at ambient temperature for half an hour. Utilizing a UV-visible spectrophotometer, the absorbance at 517&#xa0;nm was calculated. When it came to scavenging free radicals against 2,2-diphenyl1-picrylhydrazyl, NP-AuNPs exhibited the highest capacity (68.96%), followed by NP-AgNPs (41.21%), with the cell-free extract of <italic>Neodesmus pupukensis</italic> demonstrating the lowest ability (37.56%). Due to its simplicity and speed of usage, DPPH has become a useful technique for determining a compound&#x2019;s antioxidant potential. The nanoparticles exhibited a higher level of antioxidant activity in comparison to the <italic>N. pupukensis</italic> cell-free extract. This suggests that the <italic>N. pupukensis</italic> nanoparticles have better antioxidant qualities than the extract derived from cells, highlighting their potential for use in medicinal and biotechnological fields (<xref ref-type="bibr" rid="B69">Omomowo et al., 2020</xref>).</p>
<p>The antioxidant properties of the green alga extract <italic>Botryococcus braunii</italic> were assessed in order to synthesize palladium and platinum nanoparticles. Using the serial dilution approach, green algae were gathered, separated, and cultured on Chu-13 nutritional medium. Palladium and platinum nanoparticles produced by algae were categorized using scanning electron spectroscopy and X-ray diffraction. Using 1,1-diphenyl-2-picrylhydrazyl, the antioxidant activity of the nanoparticles was investigated. By measuring the DPPH free radical scavenging activity, the antioxidant ability of the green produced palladium and platinum nanoparticles was assessed. The DPPH solution eventually turned pale yellow in the presence of nanoparticles, changing from purple over time. The percentage of DPPH that was foraged grew undeviated as the nano-mediated particle density increased from 1 to 20&#xa0;&#x3bc;g/mL. For palladium, this occurred within 30&#xa0;min at 20&#xa0;&#x3bc;g/mL, while for platinum, it reached 78.14% at 25&#xa0;&#x3bc;g/mL (<xref ref-type="bibr" rid="B13">Arya et al., 2020</xref>).</p>
<p>Zinc acetate dihydrate and zinc nitrate hexahydrate were used as forerunners for the biofabrication and capping of ZnO NPs, which were made possible by the bioactive compounds found in <italic>Shyalina</italic> extract. The radical neutralizing activity of the produced ZnONPs was measured by DPPH. ZnO nanoparticles derived from algae exhibited exceptional scavenging ability (IC<sub>50</sub> &#x3d; 16.1 &#xb1; 0.74&#xa0;&#x3bc;g/mL and 18.89 &#xb1; 0.63&#xa0;&#x3bc;g/mL) in contrast to algal extract (IC<sub>50</sub> values of 21.2 &#xb1; 0.98&#xa0;&#x3bc;g/mL). A chemical with a low IC<sub>50</sub> value has a higher scavenging activity. ZnO NPs derived from algae had lower IC<sub>50</sub>values, indicating a higher potential for antioxidant activity. This could be because, following the creation of ZnO NPs, phenolic compounds were more active. Because of their strong antioxidant activity and capacity to function as reducing agents, phenolic active compounds, which are present in algal extract, are important in the production of ZnONPs (<xref ref-type="bibr" rid="B44">Hameed et al., 2023</xref>).</p>
<p>The excess biomass of the microalgae <italic>Acutodesmus dimorphus</italic> was utilized to create a micro-algal water extract following lipid extraction, which was subsequently utilized to create silver nanoparticles (2&#x2013;20&#xa0;nm) (<xref ref-type="bibr" rid="B65">Mukherjee et al., 2021</xref>). One litre of Erlenmeyer flasks holding 500 mL of dairy wastewater were used to culture <italic>A. dimorphus</italic>. After being infused (10% v/v) into the flasks, the actively growing culture of <italic>A. dimorphus</italic> was incubated at 35&#xa0;&#xb0;C with 60&#xa0;&#x3bc;mol&#xa0;m<sup>&#x2212;2</sup> s<sup>&#x2212;1</sup>. For 8&#xa0;days, there was a light-dark cycle of 12:12&#xa0;h with a light intensity (cool white fluorescent lamps). To prevent the cells from adhering to the flask surface, the flasks were manually shaken three times a day. As mentioned in the earlier study (<xref ref-type="bibr" rid="B25">Chokshi et al., 2016</xref>), the dried microalgal biomass was used to extract lipid using a chloroform: methanol (1:2, v/v) ratio. The biosynthesized silver nanoparticles&#x2019; antioxidant capacity was evaluated through the utilization of 2,20-azino-bisphosphate (3-ethylbenzothiazoline-6-sulfonic acid) (<xref ref-type="bibr" rid="B25">Chokshi et al., 2016</xref>). The utilization of 2,2&#x2032;-azino-bis(3-ethylbenzothiazoline-6-sulfonic acid) (ABTS) in evaluating the antioxidant capacity of biosynthesized silver nanoparticles, which involves:<list list-type="alpha-lower">
<list-item>
<p>ABTS Radical Cation (ABTS&#x2022;&#x2b;) Formation: When ABTS is oxidized, it produces the radical cation form (ABTS&#x2022;&#x2b;), which is the form that is most frequently employed. The maximal absorbance of this blue-green radical cation is around 734&#xa0;nm in wavelength.</p>
</list-item>
<list-item>
<p>Antioxidant Capacity Measurement: At 734&#xa0;nm, absorbance decreases when an antioxidant is present because it can return the ABTS&#x2022;&#x2b; to its neutral state. The sample&#x2019;s antioxidant capacity is directly correlated with the degree of this decline.</p>
</list-item>
<list-item>
<p>Quantification: Spectrophotometric analysis is used to measure the absorbance reduction. The antioxidant capacity is then measured in terms of Trolox equivalent antioxidant capacity (TEAC) by comparing the sample&#x2019;s drop in absorbance to that of a standard antioxidant, such as Trolox.</p>
</list-item>
</list>
</p>
<p>Given below is <xref ref-type="table" rid="T3">Table 3</xref> of nanobioparticles showing antioxidant properties relevant to SDGs:</p>
<table-wrap id="T3" position="float">
<label>TABLE 3</label>
<caption>
<p>Table showing algae mediated NPs of antioxidant properties relevant to SDGs.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Sl. No.</th>
<th align="center">Algal source</th>
<th align="center">Reagents used</th>
<th align="center">NPs produced</th>
<th align="center">References</th>
<th align="center">SDG</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">1</td>
<td align="left">
<italic>Tetraselmis indica</italic>
</td>
<td align="left">Zinc acetate; algal aqueous extract as reducing and capping agent</td>
<td align="left">ZnO</td>
<td align="left">
<xref ref-type="bibr" rid="B20">Bhakya et al. (2016)</xref>, <xref ref-type="bibr" rid="B95">Thirumoorthy et al. (2021)</xref>
</td>
<td rowspan="5" align="left">SDG 3: Good Health and Wellbeing</td>
</tr>
<tr>
<td align="left">2</td>
<td align="left">
<italic>Spirogyra hyalina</italic>
</td>
<td align="left">Zinc nitrate (Zn(NO<sub>3</sub>)<sub>2</sub>); <italic>Spirogyra</italic> extract as stabilizing agent</td>
<td align="left">ZnO</td>
<td align="left">
<xref ref-type="bibr" rid="B44">Hameed et al. (2023)</xref>
</td>
</tr>
<tr>
<td align="left">3</td>
<td align="left">
<italic>Neodesmuspupukensis</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>) and chloroauric acid (HAuCl<sub>4</sub>); algal extract as reducer and stabilizer</td>
<td align="left">AgNPs, AuNPs</td>
<td align="left">
<xref ref-type="bibr" rid="B69">Omomowo et al. (2020)</xref>
</td>
</tr>
<tr>
<td align="left">4</td>
<td align="left">
<italic>Botryococcusbraunii</italic>
</td>
<td align="left">Palladium chloride (PdCl<sub>2</sub>) and chloroplatinic acid (H<sub>2</sub>PtCl<sub>6</sub>); algal extract as reducing agent</td>
<td align="left">PdNPs, PtNPs</td>
<td align="left">
<xref ref-type="bibr" rid="B13">Arya et al. (2020)</xref>
</td>
</tr>
<tr>
<td align="left">5</td>
<td align="left">
<italic>Acutodesmusdimorphus</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as reducing and stabilizing agent</td>
<td align="left">AgNPs</td>
<td align="left">
<xref ref-type="bibr" rid="B25">Chokshi et al. (2016)</xref>, <xref ref-type="bibr" rid="B65">Mukherjee et al. (2021)</xref>
</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s4-2">
<label>4.2</label>
<title>Anti-bacterial</title>
<p>Studies on the antibacterial activity of nanoparticles stemmed fromgreen algae against many strains of bacteria. Zinc acetate was reduced utilizing a green synthesis technique, employing <italic>Tetraselmis indica</italic> algae extract as a precursor to produce ZnONPs. By using the Agar well diffusion method, it was determined that the biosynthesized ZnONPs exhibited antimicrobial actionupside topathogenic bacteria. Among the chosen bacterial strains, the most susceptible and resilient were the Gram-positive <italic>S. aureus</italic>, with a maximum zone of 18.4 &#xb1; 0.5 mm, and the Gram-negative <italic>E. coli</italic>, with a minimum zone of 12.3 &#xb1; 0.3&#xa0;mm. Since the zone of inhibition increases with increasing ZnONPs concentration, we can infer that the antibacterial property is directly correlated with the analyte concentration used. This makes sense given that a high concentration of ZnONPs will enter the bacterial cell wall, leading to more effective antibacterial activity (<xref ref-type="bibr" rid="B95">Thirumoorthy et al., 2021</xref>). <italic>Botryococcus braunii</italic> green algal extract was used to create palladium and platinum nanoparticles. Without the use of chemicals as reducing agents, algae extract seems to be a promising source of reducing and stabilizing agents. Visual inspection was used to check the entire metal nanoparticle production process at first. Two Gram-positive bacterial strains, <italic>K. pneumoniae</italic> (MTCC 109) and <italic>S. aureus</italic> (MTCC 96), and two Gram-negative bacterial strains, <italic>P. aeruginosa</italic> (MTCC 441) and <italic>E. coli</italic> (MTCC 442), were used to test the antibacterial activity of platinum and palladium nanoparticles. PtNPs and PdNPs at 400&#xa0;&#x3bc;g/mL concentration demonstrated the highest zone of inhibition against the test pathogens. The nanoparticles generated from that algal culture exhibit antibacterial activity, with a zone of inhibition spanning from 7 to 16&#xa0;mm (<xref ref-type="bibr" rid="B13">Arya et al., 2020</xref>).</p>
<p>The green-synthesized NiO nanoparticles&#x2019; antibacterial activity was tested against Gram-positive <italic>S. aureus</italic> and Gram-negative <italic>E. coli</italic>, <italic>K. pneumoniae</italic>, and <italic>P. aeruginosa</italic> pathogens utilizing the disk diffusion method. <xref ref-type="fig" rid="F5">Figures 5a,b</xref> provides the zones of inhibition (ZOI) at various concentrations of NiO nanoparticles. Research focused on the effect of silver nanoparticles on the bacterial release of intracellular components. Various concentrations of the nanoparticles were administered to <italic>P. aeruginosa</italic>, <italic>B. cereus</italic>, <italic>S. aureus</italic>, and <italic>K. pneumoniae</italic>. Increments of A<sub>260</sub> correlating to the concentration of nanoparticles were found, with <italic>P. aeruginosa</italic> yielding the greatest values at 25&#xa0;mg/mL and 1&#xa0;h of exposure, as reflected in <xref ref-type="fig" rid="F5">Figure 5d</xref>.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption>
<p>
<bold>(a)</bold> Antibacterial properties of NiO NPs on four pathogenic bacteria <bold>(b)</bold> Bar graph illustrating the inhibition zone at various concentrations of NiO NPs. Reproduced with permission from (<xref ref-type="bibr" rid="B22">Borah et al., 2020</xref>) &#xa9; Elsevier 2020. <bold>(c)</bold> Antifungal effects of Ag nano particles against selected fungal species. <bold>(d)</bold> Effect of silver nanoparticles on the integrity of cell membrane. Reproduced from (<xref ref-type="bibr" rid="B5">Al-Radadi et al., 2022</xref>), under the CC BY-NC-ND 4.0 license.</p>
</caption>
<graphic xlink:href="fnano-08-1751841-g005.tif">
<alt-text content-type="machine-generated">Four-panel image illustrating antibacterial effects of nanoparticles. (a) Agar plate tests showing inhibition zones for S. aureus, E. coli, K. pneumoniae, and P. aeruginosa at various concentrations. (b) Bar chart displaying zone diameters for different bacteria with increasing concentrations of nickel oxide nanoparticles. (c) Bar chart comparing inhibition zones of silver nanoparticles against multiple bacterial strains. (d) Line graph showing absorbance (A490) changes with varying concentrations of nanoparticles for four bacteria.</alt-text>
</graphic>
</fig>
<p>The cell-free extracts of microalgae <italic>N. pupukensis</italic> were used to create gold (AuNPs) and AgNPs. The Evaluation of antimicrobial properties from these nanoparticles was done against five different bacteria using agar well diffusion method. While NP-AuNPs were only moderately active against both <italic>Pseudomonas</italic> sp. and <italic>S. marcescens</italic>, with zone of inhibition of 27.5&#xa0;mm and 28.5 mm, respectively, AgNPs demonstrated a high antibacterial potency of 43&#xa0;mm, 24.5 mm, 27&#xa0;mm, and 39&#xa0;mm against <italic>P</italic>. <italic>aeruginosa</italic>, <italic>E. coli, K. pneumoniae</italic>, and <italic>S. marcescens</italic>, respectively<italic>. Staphylococcus aureus</italic> was inhibited by NP-AgNPs and NP-AuNPs with respective activities of 24.5 and 17.5&#xa0;mm (<xref ref-type="bibr" rid="B69">Omomowo et al., 2020</xref>).</p>
<p>Utilizing zinc acetate dihydrate and zinc nitrate hexahydrate as predecessors, <italic>Spirogyra hyaline</italic> decoction was used for the biofabrication and capping of ZnONPs. The structural and optical modifications of the novel biosynthesized ZnONPs were investigated using energy dispersive X-ray spectroscopy (EDX), X-ray diffraction (XRD), scanning electron microscopy (SEM), UV-Vis spectroscopy, and Fourier transform infrared spectroscopy (FT-IR). Among <italic>P. aeruginosa, B</italic>. <italic>pumilus, S</italic>.<italic>s aureus,</italic> and <italic>E</italic>. <italic>coli</italic>, ZnONPs [Precurssor: ZA (Zinc acetate) and ZN (Zinc nitrate)] showed different levels of activity, with distinct zones measuring 15.33 &#xb1; 0.42, 16.33 &#xb1; 1.14, 24.33 &#xb1; 1.12, and 16.67 &#xb1; 0.92 mm, in that order. The zones of inhibition against bacterial strains grew as the nanoparticle mass concentration increased. Algal-based ZnONPs showed excellent antibacterial activity in contrast to that of algal extract against the diverse strains of Gram-positive and Gram-negative bacteria. Zinc oxide NPs demonstrated substantial antibacterial activity against Gram-positive bacteria, especially <italic>S. aureus</italic> (<xref ref-type="bibr" rid="B44">Hameed et al., 2023</xref>).</p>
<p>The marine algae <italic>Caulerpa serrulata</italic> was used to create strong and colloidal-shaped silver nanoparticles, which had remarkable antibacterial efficacy against <italic>Shigella</italic> sp<italic>., S. aureus, E. coli, P. aeruginosa,</italic> and <italic>Salmonella typhi</italic> at lower doses (<xref ref-type="bibr" rid="B65">Mukherjee et al., 2021</xref>). <italic>Salmonella typhi</italic> exhibited the least zone of inhibition at 10&#xa0;mm at 50&#xa0;&#xb5;L solution of silver nanoparticles, but <italic>E. Coli</italic> had the biggest zone of inhibition at 21&#xa0;mm (<xref ref-type="bibr" rid="B1">Aboelfetoh et al., 2017</xref>).</p>
<p>AgNPs extracted from <italic>P. oedogonia</italic> aqueous extract have demonstrated promising antibacterial action against <italic>E. coli, M. luteus, S. aureus, B. subtilis, Vibrio cholerae, P. aeruginosa,</italic> and <italic>Shigella flexneri.</italic> AgNPs exhibit remarkable antibacterial efficacy against highly resistant Gram-negative rods, as demonstrated by the measurement of the maximum zone of inhibition (17.2&#xa0;mm) for <italic>P. aeruginosa</italic> (<xref ref-type="bibr" rid="B87">Sinha et al., 2015</xref>).</p>
<p>Using the disc diffusion assay, the antibacterial efficacy of <italic>C. minutissima</italic> extract-derived Ag-NPs was evaluated against possible human pathogens, including <italic>E. coli, Salmonella</italic> sp<italic>., Klebsiella</italic> sp. (Gram-negative), <italic>Bacillus cereus,</italic> and <italic>Staphylococcus aureus</italic> (Gram-positive). The greatest zone of inhibition that Ag-NPs produced against <italic>B. cereus</italic> (21 &#xb1; 1&#xa0;mm) was higher than that of <italic>S. aureus</italic> (20&#xa0;mm) and <italic>E. coli</italic> (20&#xa0;mm) among the five test bacterial species. Ag-NPs were found to be moderately effective against <italic>Salmonella</italic> spp. (17 &#xb1; 1&#xa0;mm) and <italic>Klebsiella</italic> sp. was found to be minimally vulnerable toward Ag-NPs. At pH 9, a stable and high yield of Ag-NPs was obtained with a ratio of 1:10 for the precursor metal salt solution to algal extract and a concentration of 10&#xa0;mM for AgNO<sub>3</sub> (<xref ref-type="bibr" rid="B54">Kumar et al., 2024a</xref>). Therefore, the green synthesis technique that uses algae extract instead of more traditional physical and chemical methods for the production of Ag-NPs turns out to be a cost-effective, efficient, environmentally friendly, economically viable, and long-lasting strategy. To combat antibiotic resistance, large-scale Ag-NP production is possible with <italic>C. minutissima</italic>. Utilizing these Ag-NPs can help reduce the microbial load and treat wastewater effluent and synthesize silver nanoparticles using algae (<xref ref-type="bibr" rid="B54">Kumar et al., 2024a</xref>). Given below is <xref ref-type="table" rid="T4">table 4</xref> of nanobioparticles showing antioxidant properties relevant to SDGs:</p>
<table-wrap id="T4" position="float">
<label>TABLE 4</label>
<caption>
<p>Algae mediated NPs of antibacterial properties relevant to SDGs.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">S. No</th>
<th align="left">Algal source</th>
<th align="center">Reagents used</th>
<th align="left">NPs produced</th>
<th align="left">Targeted microbes</th>
<th align="left">References</th>
<th align="left">SDG</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">1</td>
<td align="left">
<italic>Tetraselmis indica</italic>
</td>
<td align="left">Zinc nitrate as Zn precursor; algal aqueous extract as reducing/capping agent</td>
<td align="left">ZnO NPs</td>
<td align="left">
<italic>Staphylococcus aureus, Escherichia coli</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B95">Thirumoorthy et al. (2021)</xref>
</td>
<td rowspan="7" align="left">SDG 3: Good Health and Wellbeing</td>
</tr>
<tr>
<td align="left">2</td>
<td align="left">
<italic>Botryococcusbraunii</italic>
</td>
<td align="left">Palladium chloride (PdCl<sub>2</sub>) and chloroplatinic acid (H<sub>2</sub>PtCl<sub>6</sub>); algal extract as stabilizing agent</td>
<td align="left">Pd, Pt</td>
<td align="left">
<italic>Staphylococcus marcescens,</italic>
<break/>
<italic>Pseudomonas aeruginosa, Klebsiella pneumoniae, Escherichia coli</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B13">Arya et al. (2020)</xref>
</td>
</tr>
<tr>
<td align="left">3</td>
<td align="left">
<italic>Neodesmuspupukensis</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>) and chloroauric acid (HAuCl<sub>4</sub>); algal extract as reducer and stabilizer</td>
<td align="left">Ag, Au</td>
<td align="left">
<italic>Staphylococcus marcescens, Pseudomonas aeruginosa, Klebsiella pneumoniae, Escherichia coli</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B69">Omomowo et al. (2020)</xref>
</td>
</tr>
<tr>
<td align="left">4</td>
<td align="left">
<italic>Spirogyra hyalina</italic>
</td>
<td align="left">Zinc nitrate (Zn(NO<sub>3</sub>)<sub>2</sub>); <italic>Spirogyra</italic> extract as reducing and capping agent</td>
<td align="left">ZnO</td>
<td align="left">
<italic>Pseudomonas aeruginosa, Bacillus pumilus, Staphylococcus aureus, Escherichia coli</italic>,</td>
<td align="center">
<xref ref-type="bibr" rid="B44">Hameed et al. (2023)</xref>
</td>
</tr>
<tr>
<td align="left">5</td>
<td align="left">
<italic>Caulerpa serrulata</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as reducing and stabilizing agent</td>
<td align="left">Ag</td>
<td align="left">
<italic>Shigella</italic> sp.<italic>, Staphylococcus aureus, Escherichia coli, Pseudomonas aeruginosa, Salmonella typhi</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B1">Aboelfetoh et al. (2017),</xref> <xref ref-type="bibr" rid="B65">Mukherjee et al. (2021)</xref>
</td>
</tr>
<tr>
<td align="left">6</td>
<td align="left">
<italic>Pithophoraoedogonia</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal aqueous extract as bioreducing/capping agent</td>
<td align="left">Ag</td>
<td align="left">
<italic>E. coli, Micrococcus luteus, S. aureus, B. subtilis, Vibrio cholerae, P. aeruginosa,</italic> and <italic>Shigella flexneri.</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B87">Sinha et al. (2015)</xref>
</td>
</tr>
<tr>
<td align="left">7</td>
<td align="left">
<italic>C. minutissima</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as reducing and stabilizing agent</td>
<td align="left">Ag</td>
<td align="left">
<italic>E. coli, Salmonella</italic> sp<italic>., Klebsiella</italic> sp. (Gram-negative), <italic>B. cereus,</italic> and <italic>S. aureus</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B54">Kumar et al., 2024a</xref>
</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s4-3">
<label>4.3</label>
<title>Antifungal</title>
<p>The antifungal activity of AuNPs produced from algae has also been studied; however, the results of these investigations are scarce <italic>A. niger, C. albicans,</italic> and <italic>Candida parapsilosis</italic> fungal strains have all shown significant growth retardation when exposed to AgNPs biosynthesized from green algae, <italic>Ulva latica</italic> (<xref ref-type="bibr" rid="B29">Dhavale et al., 2020</xref>). Recently, some of the research groups evaluated the fungicidal activityof biosynthesized silver nanoparticles by dissolving 1&#xa0;mg of silver nanoparticles in DMSO and inoculating them with fungal isolates. The nanoparticles showed maximum zones of inhibition against <italic>F. solani</italic>, <italic>Rhizoctonia solani</italic>, and <italic>Fusarium proliferatum</italic>, as shown in <xref ref-type="fig" rid="F5">Figure 5c</xref>. The mycosis-inhibiting capacityof AgNPs and AuNPs mediated by <italic>N. pupukensis</italic> was investigated. The graded concentrations of each compound were added to potato dextrose agar plates (<xref ref-type="bibr" rid="B52">Khatami et al., 2015</xref>). These plates were then infused with a 6&#xa0;mm agar plug containing 48-hour-old cultures of five different fungi. AgNPs&#x2019; antifungal efficacy was verified by measuring their mycelial inhibition against <italic>A. niger, A. fumigatus, A. flavus, Fusarium solani, and C. albicans,</italic> which yielded 80.6%, 57.1%, 79.4%, 65.4%, and 69.8%, respectively. In contrast, AuNPs demonstrated 79.4%, 44.3%, 75.4%, 54.9%, and 66.4% against <italic>A. niger, A. fumigatus, A. flavus, F. solani, and C. albicans,</italic> respectively. NP-AgNPs (<italic>N. pupukensis&#x2013;</italic>AgNPs) exhibited the greatest mycelial inhibition against <italic>A. niger</italic> (80.6%), whereas NP-AuNPs (<italic>N. pupukensis-</italic>AuNPs) had the least inhibition against <italic>F. solani</italic> (44.3%). <italic>Neodesmus pupukensis</italic> silver and gold nanoparticles were both very effective against the toxic fungus under investigation, and some of the plates displayed mycelial inhibition (<xref ref-type="bibr" rid="B69">Omomowo et al., 2020</xref>).</p>
<p>Using green algae <italic>Botryococcus braunii</italic>, stable palladium and platinum nanoparticles were effectively created. The study examined the antifungal properties of platinum and palladium nanoparticles in relation to the fungus <italic>Fusarium oxysporum</italic> (MTCC 2087). The agar well plate method was used to assessantimycotic efficacy testing of the nanoparticles in terms of the zone of inhibition of microbial growth, and an agar dilution experiment was used to estimate the lowest inhibitory dose. From that algal culture, nanoparticles were generated, and the highest zone of inhibition against the test strains was shown by PdNPs and PtNPs at 400&#xa0;&#x3bc;g/mL concentration, with a zone of inhibition spanning from 7 to 16&#xa0;mm, which proves that nanoparticles possess antifungal activity (<xref ref-type="bibr" rid="B13">Arya et al., 2020</xref>).</p>
</sec>
<sec id="s4-4">
<label>4.4</label>
<title>Anti-biofilm activity</title>
<p>The green synthesis of silver nanoparticles (AgNPs) using filamentous algae extract of <italic>Spirogyra</italic> sp has demonstrated anti-biofilm properties against nosocomial pathogens, specifically <italic>Staphylococcus aureus</italic> and <italic>Acinetobacter baumannii</italic>. The biosynthesized AgNPs exhibit a spherical morphology with sizes ranging from 20 to 30&#xa0;nm and display significant biofilm formation of the tested bacterial strains. Characterization techniques such as UV-Vis spectroscopy, XRD, and FTIR analyses confirmed the successful creation of AgNPs and indicated their interactions with phytochemicals in the algae extract (<xref ref-type="bibr" rid="B27">Danaei et al., 2021</xref>).</p>
<p>The following study has shown the potential of lutein, a carotenoid extracted from the green microalga <italic>Chlorella pyrenoidosa</italic>, as an antibiofilm and quorum-sensing agent against <italic>Pseudomonas aeruginosa</italic>, a pathogenic bacterium known for its resistance to antibiotics and ability to form biofilms. The study has also demonstrated that nutrient starvation enhances lutein production, which significantly inhibits biofilm formation and disrupts quorum-sensing mechanisms in <italic>P. aeruginosa</italic>. Through high-performance liquid chromatography (HPLC) and molecular docking studies, the research reveals that lutein interacts with key proteins involved in the quorum sensing system, leading to the downregulation of relevant genes. The findings suggest that lutein could be a valuable natural alternative for treating infections associated with biofilm-forming bacteria, particularly in cases where conventional antibiotics are ineffective (<xref ref-type="bibr" rid="B81">Sampathkumar et al., 2019</xref>). The interaction of nanoparticles with bacterial membranes and the consequent release of internal cellular components was evaluated by absorbance measurement at 260&#xa0;nm as shown in <xref ref-type="fig" rid="F5">Figure 5d</xref>. For 1&#xa0;h and at 25, 35, and 45&#xa0;&#x3bc;g/mL, silver nanoparticles were exposed with <italic>P. aeruginosa</italic>, <italic>Bacillus cereus</italic>, <italic>S. aureus</italic>, and <italic>Klebsiella pneumoniae</italic>. An increase of the A260 values was noted for all bacteria in relation to the concentration, and this indicates further membrane disruption and intracellular leakage.</p>
<p>The anti-biofilm potential of sulfated polysaccharides (SPs) derived from <italic>Chlamydomonas reinhardtii</italic> against the foodborne pathogens <italic>Salmonella enterica</italic> and <italic>Vibrio harveyi</italic>, isa significant contributor to foodborne diseases and antibiotic resistance. Cr-SPs effectively inhibit both planktonic growth and biofilm formation of these bacteria in a dose-dependent manner, with notable reductions in metabolic activity and extracellular polysaccharide production. The ability of Cr-SPs to not only prevent biofilm formation but also to eradicate preformed biofilms suggests their potential as a natural alternative therapeutic agent in combating bacterial infections associated with foodborne illnesses (<xref ref-type="bibr" rid="B99">Vishwakarma and Vavilala, 2019</xref>).</p>
<p>The green synthesis of zinc oxide nanoparticles (ZnONPs) utilizing methanol extract from <italic>Spirulina platensis</italic>, emphasizes their characterization and potential biomedical applications. The various analytical techniques, including FE-SEM, TEM, FTIR, and XRD, were used to assess the nanoparticles&#x2019; morphology, size distribution, and crystalline structure. The antibacterial efficacy of the synthesized ZnONPs is evaluated against standard bacterial strains such as <italic>S. aureus</italic>, <italic>Streptococcus pyogenes</italic>, <italic>Salmonella typhi</italic>, and <italic>K. pneumoniae</italic>, using methods like the Agar well diffusion assay and microtiter plate assays for biofilm quantification. Results demonstrated significant antibacterial and antibiofilm activity, particularly at sub-MIC concentrations, alongside a dose-dependent cytotoxic effect on Vero cells assessed through the MTT assay (<xref ref-type="bibr" rid="B4">Ahmed and Othman, 2024</xref>).</p>
<p>The potential of lipid extracts from <italic>S platensis</italic> as anti-biofilm agents against <italic>Candida</italic> sp. <italic>is</italic> a significant contributor to chronic wound infections. By optimizing extraction conditions using bio-sourced solvents, it was successfully isolated free fatty acids (FFA) were successfully isolated, demonstrating substantial antimicrobial activity, achieving up to 80% inhibition of biofilm growth at low concentrations. The encapsulation of these lipid extracts in copper-alginate nanocarriers not only enhanced their anti-biofilm efficacy but also ensured safety for keratinocyte cells, indicating compatibility for topical applications (<xref ref-type="bibr" rid="B23">Boutin et al., 2019</xref>).</p>
</sec>
<sec id="s4-5">
<label>4.5</label>
<title>Haemolytic activity</title>
<p>Biologically synthesized nanomaterials designed for biomedical and environmental applications require assessment of hemocompatibility as part of the safety evaluation process. Algae-mediated green synthesis of nanoparticles is eliciting considerable interest for the eco-friendly and biocompatible phytochemicals which may affect blood compatibility. ZnO as an example of algae-derived metal oxide nanoparticles, is often assumed to be safe, but can under certain conditions interact with red blood cells (RBCs). Therefore, hemolytic assessment is critical for algae-derived nanoparticles. The larger probability of haemolytic activity was detected in 100&#xa0;mg mL&#x2212;1, indicating that when the ZnO nanoparticles come into surface contact with the RBC cells, haemoglobin is released into the blood plasma (<xref ref-type="bibr" rid="B76">Raja et al., 2014</xref>). Haemolysis, morphological traits, and osmotic fragility were considered when examining ZnONPs&#x2019; impact on RBCs. RBC fragility is caused by osmotic and mechanical stress on the membrane. Haemolysis of cleaned red blood cells was found to be safe within the 50&#xa0;mg mL&#x2212;1 range. This demonstrates that there will be negative health impacts from increased ZnO NPs concentrations. As a result, it makes sense that the produced ZnONPs&#x2019; haemolytic activity would depend on concentration (<xref ref-type="bibr" rid="B95">Thirumoorthy et al., 2021</xref>). It was found that very less studies were found on green algae nanoparticles, which can mediate hemolytic activity, whereas different studies on other algal classes like blue-green algae, red algae and brown algae were abundant.</p>
</sec>
<sec id="s4-6">
<label>4.6</label>
<title>Anti-cancerous activity</title>
<p>The <italic>in vitro</italic> anticancer potential of gold nanoparticles (AuNPs) synthesized using <italic>Chaetomorpha linum</italic> was demonstrated against the human colon cancer cell line HCT-116. Treatment of cancer cells with these AuNPs resulted in dose-dependent cytotoxic effects. Further analysis revealed the induction of apoptosis, marked by the activation of caspase-3 and caspase-9 and a significant reduction in anti-apoptotic proteins such as Bcl-xl and Bcl-2. These findings clearly validate the effectiveness of algal-mediated AuNPs as potential anticancer agents (<xref ref-type="bibr" rid="B2">Acharya et al., 2021</xref>). Similarly, the cytotoxic potential of green-synthesized silver nanoparticles (AgNPs) derived from the marine green alga <italic>Chaetomorpha ligustica</italic> has been reported. The biosynthesis of AgNPs was confirmed through visual color change and characterized using UV&#x2013;Vis spectroscopy and transmission electron microscopy. Notably, the synthesized AgNPs exhibited significantly higher cytotoxic activity against human colon cancer cell lines HT-29 and HCT-116 compared to the algal extract alone. These results highlight the superior anticancer efficacy of biogenic nanoparticles and their promise for future cancer research and therapeutic applications (<xref ref-type="bibr" rid="B109">Al-Zahrani et al., 2021</xref>). In another study, gold nanoparticles synthesized <italic>via</italic> green methods using the aqueous extract of the halotolerant microalga Dunaliella salina were characterized by UV&#x2013;Vis spectroscopy, transmission electron microscopy (TEM), and Fourier-transform infrared spectroscopy (FTIR), confirming the formation of stable, spherical nanoparticles. The <italic>in vitro</italic> anticancer evaluation demonstrated selective cytotoxicity of these AuNPs against the breast cancer cell line MCF-7, while exhibiting minimal toxicity toward normal breast epithelial cells (MCF-10A). This selective action suggests their potential as safer alternatives to conventional chemotherapeutic agents such as cisplatin (<xref ref-type="bibr" rid="B108">Singh et al., 2019</xref>). More recently, <xref ref-type="bibr" rid="B92">Sudhakar et al. (2025)</xref> investigated the anticancer efficacy of zirconium oxide nanoparticles synthesized using <italic>U. lactuca</italic> against the A549 lung cancer cell line. Cells treated with <italic>U. lactuca</italic>-derived ZrO<sub>2</sub> nanoparticles (UL-ZrO<sub>2</sub>NPs) showed pronounced morphological changes, including cell shrinkage and loss of structural integrity. These alterations provided clear evidence of the anticancer activity of UL-ZrO<sub>2</sub>NPs.</p>
<p>
<xref ref-type="fig" rid="F6">Figure 6</xref> examines the anticancer activity of zirconium oxide nanoparticles (ZrO<sub>2</sub>NPs) made with the extract of Ulva lactuca. The images depict a concentration-dependent cytotoxic effect of zirconium oxide nanoparticles due to changes in cellular morphology, a decrease in the density of cells, and an increase in the number of dead cells at higher concentrations.</p>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption>
<p>Anti-cancer effect of zirconium oxide nanoparticles synthesized by<italic>Ulva lactuca</italic> extract, <bold>(a)</bold> control, <bold>(b)</bold> 100&#xa0;&#x3bc;g/mL, <bold>(c)</bold> 150&#xa0;&#x3bc;g/mL, <bold>(d)</bold> 200&#xa0;&#x3bc;g/mL, <bold>(e)</bold> 250&#xa0;&#x3bc;g/mL, <bold>(f)</bold> Etoposide-treated cells, ZrO<sub>2</sub>NPs show cytotoxicity activity. Reproduced with permission from (<xref ref-type="bibr" rid="B92">Sudhakar et al., 2025</xref>), &#xa9; Elsevier 2025.</p>
</caption>
<graphic xlink:href="fnano-08-1751841-g006.tif">
<alt-text content-type="machine-generated">Microscopic images labeled a to f show varying densities of elongated cells on a flat surface. Image b has the highest cell density, while images c and e exhibit clusters. Images a, d, and f show scattered cells with fewer clusters.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s4-7">
<label>4.7</label>
<title>Drug delivery</title>
<p>Green algae-based nanoparticles are an emerging and promising area of research in drug delivery systems. These nanoparticles, synthesized using extracts from green algae, have demonstrated remarkable potential in targeting specific cells for precise drug delivery. By functionalizing the surface of these nanoparticles, they can be engineered to selectively bind to target cells, such as cancer cells, thereby enhancing the therapeutic efficacy of drugs while reducing off-target effects and minimizing side effects. Their intrinsic biocompatibility and biodegradability make them safer alternatives to conventional synthetic nanocarriers, as they are less likely to trigger immune responses or toxicity in the body. Moreover, green algae-mediated nanoparticles can improve drug solubility, stability, and bioavailability, which is especially advantageous for oral and systemic drug delivery. Polysaccharides ulvan extracted from green algae <italic>Ulva</italic>, serve as natural biopolymeric precursors due to their unique physicochemical properties, non-toxicity and abundance. These polysaccharides can be formulated into polysaccharide nanomaterials (PNMs) that encapsulate drugs efficiently, allowing sustained and controlled release, protection from premature degradation, and targeted delivery to specific tissues or cells (<xref ref-type="bibr" rid="B107">Drori et al., 2024</xref>). Additionally, the sulfated polysaccharides from <italic>Ulva</italic>, composed primarily of rhamnose, uronic acids, and xylose, exhibit intrinsic bioactivity, such as antioxidant, anti-inflammatory, and anticancer properties, which can synergistically enhance the therapeutic outcomes of the loaded drugs. This dual function as both a delivery vehicle and a bioactive agent makes green algae-mediated nanoparticles a versatile and highly promising platform for next-generation drug delivery systems, particularly in oncology, antimicrobial therapy and other targeted biomedical applications.</p>
</sec>
<sec id="s4-8">
<label>4.8</label>
<title>Nano-bioremediation</title>
<p>Green algae mediated nanoparticles (NPs) have emerged as versatile agents for environmental remediation and biomedical applications due to their unique catalytic, biocompatible and sustainable properties. Under visible light, silver nanoparticles (AgNPs) generated by Ulva lactuca photocatalyzed the degradation of methyl orange dye. In addition, a low dosage of <italic>U. lactuca</italic> mediated AgNPs significantly reduced the population of Plasmodium falciparum, a species normally resistant to chloroquine (<xref ref-type="bibr" rid="B106">Kumar et al., 2013</xref>). Similarly, hazardous pollutants such as methyl orange and methylene blue were efficiently degraded by Chlorella ellipsoidea-mediated biomatrix-loaded AgNPs, and the catalytic efficiency remained stable even after three reduction cycles (<xref ref-type="bibr" rid="B22">Borah et al., 2020</xref>). In another study, lipid-cadmium sulfide nanoparticles were synthesized using the green algae Scenedesmus obliquus. During the synthesis process, a chemisorbed monolayer of Cd<sup>2&#x2b;</sup> ions irreversibly bonded to the algal biomass, reflecting a significant increase in the adsorption kinetics of Cd<sup>2&#x2b;</sup> ions. This excellent retention capability makes Scenedesmus an effective model alga for the bioremediation of heavy metals. Various algae mediated nanoparticles have also been employed to remediate a wide range of organic and aromatic chemicals, heavy metals, and dyes. Unlike traditional chemical remediation methods, nano-bioremediation operates at the molecular level, enabling precise targeting of pollutants while preserving surrounding flora and fauna. Moreover, the biocompatibility and biodegradability of algae-based nanoparticles minimize the risk of secondary pollution, making this approach a sustainable solution for environmental cleanup. By leveraging the natural properties of green algae along with nanotechnology, nano-bioremediation provides a low-impact, high-efficiency strategy for restoring polluted environments (Suarez et al., 2025).</p>
<p>
<xref ref-type="bibr" rid="B92">Sudhakar et al. (2025)</xref> have investigated the capability of zirconium oxide nanoparticles from <italic>U. lactuca</italic> for the degradation of pollutants like Malachite Green (MG) and Eosine (E). Under sunlight irradiation, the photocatalytic degradation of MG was 93.6% of MG and 86.2% of E, as shown in <xref ref-type="fig" rid="F7">Figures 7.a,b</xref>, respectively, after 180&#xa0;min. After treatment with UV-ZrO<sub>2</sub>NPs, the peak of MG and E stayed the same. Therefore, the green chemistry applied to generate UL-ZrO<sub>2</sub>NPs from <italic>U. lactuca</italic> clearly proved the photocatalytic activity at 180&#xa0;min. <xref ref-type="table" rid="T5">Table 5</xref> summarize the microbial and pollutants removal by using algal species.</p>
<fig id="F7" position="float">
<label>FIGURE 7</label>
<caption>
<p>Photo-catalytic degradation of pollutants like <bold>(a)</bold> Malachite Green (MG) and <bold>(b)</bold> Eosine (E) by ZrO2NPs synthesized by U. lactuca. Reproduced with permission from (Sudhakar et al., 2025), &#x00A9; Elsevier 2025.</p>
</caption>
<graphic xlink:href="fnano-08-1751841-g007.tif">
<alt-text content-type="machine-generated">Two graphs and bar charts depicting dye degradation over time. Graph (a) shows absorbance spectra and a bar chart for malachite green, with colors shifting from blue to clear over 180 minutes. Graph (b) shows similar data for eosin, with colors shifting from orange to pink over 180 minutes. Each bar chart indicates increasing percentage of degradation over time.</alt-text>
</graphic>
</fig>
<table-wrap id="T5" position="float">
<label>TABLE 5</label>
<caption>
<p>Green algal-mediated nanoparticles for microbial and pollutant remediation aligned with SGDs (<xref ref-type="bibr" rid="B97">Tonelli et al., 2023</xref>).</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Nanoparticles</th>
<th align="center">Algae material used in the green synthesis protocol</th>
<th align="center">Reagent used</th>
<th align="center">Pollutant(s)remediated</th>
<th align="center">References</th>
<th align="center">SDG</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="8" align="left">AgNPs</td>
<td align="left">
<italic>Chlorella vulgaris</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as reducing/capping agent</td>
<td align="left">
<italic>Escherichia coli, Streptococcus</italic> sp., <italic>S. aureus</italic> and its methicillin-resistant strain</td>
<td align="center">
<xref ref-type="bibr" rid="B6">Aldayel et al. (2022)</xref>
</td>
<td rowspan="13" align="center">SDG 3: Good Health and Wellbeing<break/>SDG 6: Clean Water and Sanitation</td>
</tr>
<tr>
<td align="left">
<italic>Caulerpa serrulata</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as bioreducing agent</td>
<td align="left">
<italic>E. coli, P. aeruginosa, Salmonella typhi, Shigella</italic> sp<italic>.</italic> and <italic>S. aureus</italic>
<break/>Congo red</td>
<td align="center">
<xref ref-type="bibr" rid="B1">Aboelfetoh et al. (2017)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Chlorella ellipsoidea</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as reducer/stabilizer</td>
<td align="left">Methyl orange and methylene blue</td>
<td align="center">
<xref ref-type="bibr" rid="B22">Borah et al. (2020)</xref>
</td>
</tr>
<tr>
<td rowspan="2" align="left">
<italic>Caulerpa racemosa</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as reducing agent</td>
<td align="left">Methylene blue</td>
<td align="center">
<xref ref-type="bibr" rid="B31">Edison et al. (2016)</xref>
</td>
</tr>
<tr>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as reduce</td>
<td align="left">
<italic>Proteus mirabilis</italic> and <italic>S. aureus</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B50">Kathiraven et al. (2015)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Ulva flexuosa</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as reducing/capping agent</td>
<td align="left">
<italic>P. aeruginosa, E. coli, S. aureus</italic>, and <italic>Bacillus subtilis</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B30">Dixit et al. (2018)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Coelastrellaaeroterrestrica</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as bioreducing agent</td>
<td align="left">
<italic>S. aureus, Streptococcus pyogenes, B. subtilis, E. coli,</italic> and <italic>P. aeruginosa</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B45">Hamida et al. (2020)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Ulva intestinalis</italic>
</td>
<td align="left">Silver nitrate (AgNO<sub>3</sub>); algal extract as reducing/stabilizing agent</td>
<td align="left">
<italic>Candida albicans, Candida krusei, Candida tropicalis, E. coli, S. typhi, S. aureus,</italic> and <italic>Vibrio cholera</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B78">Raju et al. (2017)</xref>
</td>
</tr>
<tr>
<td rowspan="3" align="left">FeNPs</td>
<td align="left">
<italic>Ulva lactuca</italic>
</td>
<td align="left">Ferric chloride (FeCl<sub>3</sub>) or ferrous sulfate (FeSO<sub>4</sub>); algal extract as reducer</td>
<td align="left">
<italic>E. coli, S. typhimurium, Bacillus cereus, P. vulgaris</italic>, and <italic>S. aureus</italic>
</td>
<td align="center">
<xref ref-type="bibr" rid="B19">Bensy et al. (2022)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Chlorococcum</italic> sp.</td>
<td align="left">Ferric chloride (FeCl<sub>3</sub>); algal extract as reducing agent</td>
<td align="left">Cr<sup>6&#x2b;</sup>
</td>
<td align="center">
<xref ref-type="bibr" rid="B91">Subramaniyam et al. (2015)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Ulva fasciata</italic>
</td>
<td align="left">Ferric chloride (FeCl<sub>3</sub>); algal extract as stabilizer/reducer</td>
<td align="left">Biofilm-forming bacteria</td>
<td align="center">
<xref ref-type="bibr" rid="B79">Safarkar et al. (2020)</xref>
</td>
</tr>
<tr>
<td rowspan="2" align="left">AuNPs</td>
<td align="left">
<italic>Chlorella vulgaris</italic>
</td>
<td align="left">Chloroauric acid (HAuCl<sub>4</sub>); algal extract as bioreducing agent</td>
<td align="left">
<italic>E. coli, S. aureus</italic> including its methicillin-resistant strain and <italic>Streptococcus</italic> sp.</td>
<td align="center">
<xref ref-type="bibr" rid="B6">Aldayel et al. (2022)</xref>
</td>
</tr>
<tr>
<td align="left">
<italic>Chlorella vulgaris</italic>
</td>
<td align="left">Chloroauric acid (HAuCl<sub>4</sub>); algal extract as reducing/capping agent</td>
<td align="left">Pb, Zn</td>
<td align="center">
<xref ref-type="bibr" rid="B3">Adenigba et al. (2020)</xref>
</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s4-9">
<label>4.9</label>
<title>Applications in food technology and food preservation</title>
<p>Nanoparticles derived from green algae have attracted substantial attention in food technology and preservation because of their peculiar traits, such as biocompatibility, antimicrobial activity, and antioxidant potential. Green algae-based nanoparticles can be incorporated into food packaging materials to constrain the development of pathogenic microorganisms, extending the shelf life of perishable foods. For example, silver nanoparticles synthesized from green algae have shown strong antimicrobial activity against foodborne pathogens like <italic>E. coli</italic> and <italic>Salmonella</italic> (<xref ref-type="bibr" rid="B50">Kathiraven et al., 2015</xref>). Green algae-based nanoparticles can be used in biosensors for the detection of food contaminants, such as heavy metals and pesticides, ensuring food safety (<xref ref-type="bibr" rid="B53">Kumar and Chen, 2008</xref>). Green algae-derived nanoparticles can offer a sustainable and eco-friendly approach to enhancing food preservation, packaging, and safety. Their antimicrobial, antioxidant, and nutrient delivery properties make them promising candidates for various applications in food technology. The successful synthesis of ZnONPs, with a mean size of 77.81 nm, characterized by flower and sphere shapes, was obtained using <italic>Ulva fasciata</italic> extract as a reducing and stabilizing agent. The nanoparticles exhibited strong antibacterial activity against foodborne pathogens such as <italic>Escherichia coli</italic> and <italic>Staphylococcus aureus</italic>, with the bactericidal effect being time-dependent and more potent than annealed ZnONPs. When applied to peeled shrimp during refrigerated storage, the ZnONPs significantly reduced microbial loads and maintained acceptable sensory attributes (appearance, odor, color, and texture) over 6&#xa0;days. <italic>Ulva fasciata</italic>-derived ZnONPs can be a potential eco-friendly and effective bio-preservative for seafood, offering a sustainable alternative to conventional preservation methods (<xref ref-type="bibr" rid="B8">Alsaggaf et al., 2021</xref>).</p>
</sec>
<sec id="s4-10">
<label>4.10</label>
<title>Development of sustainable nanomaterials using green algae</title>
<p>Sustainability can be achieved using green algae through their versatile applications in synthesizing eco-friendly nanoparticles (NPs) with significant roles in potable water (SDG 6), economic energy (SDG 7), hunger elimination (SDG 2), and climate strategies (SDG 13). Green algae-mediated NPs, such as silver (AgNPs) and zinc oxide (ZnO NPs), are utilized for water purification, removing pollutants and pathogens, and enhancing biofuel production efficiency, offering sustainable alternatives to fossil fuels (<xref ref-type="bibr" rid="B65">Mukherjee et al., 2021</xref>). In agriculture, these NPs improve crop yields and soil health, reducing the need for chemical fertilizers, thus addressing food security challenges (<xref ref-type="bibr" rid="B20">Bhakya et al., 2016</xref>; <xref ref-type="bibr" rid="B44">Hameed et al., 2023</xref>). Additionally, green algae contribute to carbon sequestration and pollution reduction, aiding in climate change mitigation (<xref ref-type="bibr" rid="B60">Mata et al., 2010</xref>; <xref ref-type="bibr" rid="B67">Olabi et al., 2023</xref>). Despite challenges like scalability and economic viability, green algae-based NPs represent a promising, sustainable solution for global environmental and health challenges.</p>
</sec>
</sec>
<sec id="s5">
<label>5</label>
<title>Opportunities and challenges</title>
<p>Green algae nanoparticles are an intriguing field of study with many opportunities and challenges. Green algae nanoparticles are effective in removing contaminants like dyes, phenols, and organosulfur compounds from water, in which they offer a sustainable alternative to traditional methods (<xref ref-type="bibr" rid="B71">Premarathna et al., 2024</xref>). These nanoparticles have potential uses in biosensors, antibacterial, antifungal, and anticancer agents. In agriculture, green algae nanoparticles can be used as biofertilizers and biopesticides. They improve soil amendmentby providing nutritive and stimulating microbial populations. Additionally, they can help in disease resistance and enhanced crop yield (<xref ref-type="bibr" rid="B90">Sowmiya et al., 2024</xref>). Green algae nanoparticles can be used in the development of sustainable energy solutions. They can enhance the efficacy of solar cells and contribute to the production of biofuels, supporting the transition to renewable energy sources. In the industrial sector, green algae nanoparticles can be used in the production of biofuels. They can help in the conversion of biomass into bioethanol and biodiesel. Additionally, they can be used in bioremediation processes to clean up oil spills and other environmental contaminants (<xref ref-type="bibr" rid="B83">Shahid et al., 2020</xref>).</p>
<p>While the opportunities are vast, there are challenges that need to be addressed, such as scalability, economic viability, and regulatory approval. Current research and development are crucial to overcoming these hurdles and fully realizing the potential of green algae nanoparticles. Scaling up the production of green algae nanoparticles from laboratory to industrial scale is a significant challenge. Predicting the properties and behaviors of nanoparticles can be difficult. The cost of producing green algae nanoparticles can be high, making it difficult to compete with traditional materials and methods. Finding cost-effective production methods and ensuring economic viability is crucial for widespread adoption. Integrating green algae nanoparticles into existing systems and processes can be challenging. This requires collaboration between researchers, industry professionals, and policymakers to develop compatible technologies and applications. Navigating the regulatory landscape for new nanomaterials can be complex and time-consuming. Obtaining approval from regulatory bodies for the use of green algae nanoparticles in various applications requires extensive testing and documentation (<xref ref-type="bibr" rid="B83">Shahid et al., 2020</xref>). Public awareness and perception of nanotechnology can impact the adoption of green algae nanoparticles. Educating the public and stakeholders about the benefits and safety of these nanoparticles is essential to gain acceptance. Developing standardized procedures for the synthesis, classification, and uses of green algae nanoparticles is necessary to ensure consistency and reliability. This includes establishing guidelines for quality control and safety measures.</p>
</sec>
<sec id="s6">
<label>6</label>
<title>Future prospects</title>
<p>The prospects of green algae-based nanoparticles are highly promising, with ongoing research and development driving innovative applications. These nanoparticles are predictedtoplay a vital role in environmental sustainability. Their potential for removing pollutants from water and soil, coupled with their role in bioremediation, will contribute to cleaner ecosystems and a reduction in environmental impact. In the medical field, green algae-based nanoparticles are being investigated for their use in targeted drug delivery, antioxidant activity, and tissue engineering. Their inherent biocompatibility, combined with the capability to selectively target specific sites within the body, makes them highly promising candidates for the design of advanced therapeutic treatments.</p>
<p>In agriculture, these nanoparticles are anticipated to revolutionize farming practices by functioning as biofertilizers and biopesticides. They hold the potential to enhance soil health, greater harvests, and decrease dependence on chemical soil conditioners and pesticides, promoting sustainable agricultural practices. Additionally, green algae nanoparticles may significantly improve the efficiency of solar cells, contributing to the advancement of sustainable energy solutions. Their capacity to convert sunlight and carbon dioxide into energy makes them important in the development of renewable energy technologies.</p>
<p>Furthermore, these nanoparticles are expected to aid in biofuel production and bioremediation processes. They can facilitate the conversion of biomass into bioethanol and biodiesel, while also assisting in cleaning up oil spills and other environmental contaminants. Ongoing research is focused on overcoming challenges related to scalability, economic feasibility, and regulatory approval. Key areas of interest include the development of standardized protocols and the optimization of production methods to fully unlock the potential of green algae nanoparticles. The future of green algae-based nanoparticles appears promising, with their sustainable and versatile nature offering numerous opportunities across diverse sectors.</p>
</sec>
<sec sec-type="conclusion" id="s7">
<label>7</label>
<title>Conclusion</title>
<p>In this study, the potential of sustainable generation of NPs from green algae, which serves as a biological platform, is evaluated. The review also depicts the algae&#x2019;s distinct physicochemical traits, eco-friendly synthesis pathways, including a wide range of implementation in biomedicine, agriculture, remediation, energy, and food technology. Linking algae nanotechnology to the UN SDGs is one of the research&#x2019;s primary objectives. Accordingly, green algae-based NPs offer a basis to achieve SDG six involving wastewater treatment, efficient pollutant removal and antimicrobial activity. In regard to SDG 7, it also amplifies solar power and aids in the production of biofuel, through increased lipid accumulation and catalytic conversion of algal biomass into renewable fuels, thus providing a source of affordable and clean energy. They advocate in SDG 2, which emphasizes Zero hungerowingto their role in increasing crop yield, soil fertility, and nutrient bioavailability. In addition, they are directly adhered to SDG 13because of their proficient photosynthetic capability and effectiveness for carbon sequestration. These efficacies showcase algae-mediated nanoparticles as a sustainability tool with cross-sectoral and global implications for scientificadvancement. Despite the innovative proficiencies of nanotechnology progress, the translation of laboratory-scale (a minuscule scale) implications into industrial integration still poses a major challenge. Importantly, issues focusing on safety, liability, scalability and their cost-effectiveness need to be addressed before the adoption and commercialization ofalgae-based NPs. In fact, the regulatory uncertainties concerning nanomaterial safety and their environmental interactions should be meticulously screened. Another hurdle can be the public perception of nanotechnology products. Addressing these hurdles would require interdisciplinary collaborations that span across nanotechnology, environmental science and government policies. Future studies should extensively emphasize improving the modus operandi of nanoparticle synthesis, as various factors determine their catalytic and biological activities. With the advancement in technology, investigation in the algal-based nano field could ascertain a world that is more resilient towards emerging challenges.</p>
</sec>
</body>
<back>
<sec sec-type="author-contributions" id="s8">
<title>Author contributions</title>
<p>MD: Methodology, Formal Analysis, Writing &#x2013; original draft, Investigation, Data curation. TM: Software, Investigation, Writing &#x2013; original draft, Data curation, Methodology, Formal Analysis. MS: Investigation, Writing &#x2013; original draft, Formal Analysis, Data curation. KS: Investigation, Data curation, Methodology, Writing &#x2013; original draft. BM: Data curation, Methodology, Writing &#x2013; original draft, Investigation, Software. SR: Validation, Resources, Writing &#x2013; review and editing. NS: Validation, Investigation, Visualization, Resources, Funding acquisition, Conceptualization, Data curation, Project administration, Formal Analysis, Methodology, Writing &#x2013; review and editing, Software, Writing &#x2013; original draft, Supervision. YM: Writing &#x2013; review and editing, Software, Writing &#x2013; original draft, Investigation, Resources, Visualization, Funding acquisition, Formal Analysis, Validation, Data curation, Supervision, Methodology, Project administration, Conceptualization.</p>
</sec>
<ack>
<title>Acknowledgements</title>
<p>The authors extend their sincere appreciation to their respective institutions for providing facilities to develop this manuscript.</p>
</ack>
<sec sec-type="COI-statement" id="s10">
<title>Conflict of interest</title>
<p>The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="ai-statement" id="s11">
<title>Generative AI statement</title>
<p>The author(s) declared that generative AI was not used in the creation of this manuscript.</p>
<p>Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.</p>
</sec>
<sec sec-type="disclaimer" id="s12">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
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<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/72863/overview">Jiang Wei</ext-link>, Tulane University, United States</p>
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<fn fn-type="custom" custom-type="reviewed-by">
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<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2238876/overview">Paula Barciela</ext-link>, University of Vigo, Spain</p>
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<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3303946/overview">Abin Joshy</ext-link>, Tulane University, United States</p>
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<fn-group>
<fn fn-type="abbr" id="abbrev1">
<label>Abbreviations:</label>
<p>AgNPs, Silver Nanoparticles; AuNPs, Gold Nanoparticles; SiNPs, Silica Nanoparticles; PtNPs, Platinum Nanoparticles; PdNPs, Palladium Nanoparticles; ZnO NPs, Zinc Oxide Nanoparticles; TiO<sub>2</sub> NPs, Titanium dioxide Nanoparticles; Fe<sub>3</sub>O<sub>4</sub> NPs, Iron Oxide Nanoparticles; CuO NPs, Copper Oxide Nanoparticles; Sph, Spherical; Tri, Triangular; Rob, Robust; Col, Colloidal; Coa, Coalescence; Rou, Round; Rec, Rectangular; Ico, Icosahedral; Cir, Circular; Hex, Hexagonal; N Tri, Nano Triangles; FCC, Face Centered Cubic.</p>
</fn>
</fn-group>
</back>
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