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<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Nanotechnol.</journal-id>
<journal-title>Frontiers in Nanotechnology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Nanotechnol.</abbrev-journal-title>
<issn pub-type="epub">2673-3013</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-meta>
<article-id pub-id-type="publisher-id">1621024</article-id>
<article-id pub-id-type="doi">10.3389/fnano.2025.1621024</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Nanotechnology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Impact of green synthesized selenium nanoparticles on the growth and development of amaranth microgreens</article-title>
<alt-title alt-title-type="left-running-head">Gomathi 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.2025.1621024">10.3389/fnano.2025.1621024</ext-link>
</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Gomathi</surname>
<given-names>Arivalagan</given-names>
</name>
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<sup>1</sup>
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<contrib contrib-type="author">
<name>
<surname>Sriharini</surname>
<given-names>Ramalingam</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
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<contrib contrib-type="author">
<name>
<surname>Arumuka Pravin</surname>
<given-names>Iyadurai</given-names>
</name>
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<sup>1</sup>
</xref>
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<contrib contrib-type="author">
<name>
<surname>Kaushik</surname>
<given-names>Rajaram</given-names>
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<xref ref-type="aff" rid="aff2">
<sup>2</sup>
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<contrib contrib-type="author">
<name>
<surname>Ramesh Kumar</surname>
<given-names>Alagarsamy</given-names>
</name>
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<sup>1</sup>
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<contrib contrib-type="author">
<name>
<surname>Anbu Sezhian</surname>
<given-names>Ambethgar</given-names>
</name>
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<sup>1</sup>
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<contrib contrib-type="author" corresp="yes">
<name>
<surname>Srivignesh</surname>
<given-names>Sundaresan</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
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<aff id="aff1">
<sup>1</sup>
<institution>Department of Horticulture</institution>, <institution>School of Life Sciences</institution>, <institution>Central University of Tamil Nadu</institution>, <addr-line>Thiruvarur</addr-line>, <addr-line>Tamil Nadu</addr-line>, <country>India</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Department of Microbiology</institution>, <institution>School of Life Sciences</institution>, <institution>Central University of Tamil Nadu</institution>, <addr-line>Thiruvarur</addr-line>, <addr-line>Tamil Nadu</addr-line>, <country>India</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>
<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/129250/overview">Jayanta Kumar Patra</ext-link>, Dongguk University Seoul, Republic of Korea</p>
</fn>
<fn fn-type="edited-by">
<p>
<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/406705/overview">Ilika Ghosh</ext-link>, Max Planck Florida Institute for Neuroscience (MPFI), United States</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1018458/overview">Zienab F. R. Ahmed</ext-link>, United Arab Emirates University, United Arab Emirates</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3078083/overview">Rupesh Kumar</ext-link>, O. P. Jindal Global University, India</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Sundaresan Srivignesh, <email>srivignesh@cutn.ac.in</email>
</corresp>
</author-notes>
<pub-date pub-type="epub">
<day>24</day>
<month>07</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2025</year>
</pub-date>
<volume>7</volume>
<elocation-id>1621024</elocation-id>
<history>
<date date-type="received">
<day>30</day>
<month>04</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>25</day>
<month>06</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2025 Gomathi, Sriharini, Arumuka Pravin, Kaushik, Ramesh Kumar, Anbu Sezhian and Srivignesh.</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Gomathi, Sriharini, Arumuka Pravin, Kaushik, Ramesh Kumar, Anbu Sezhian and Srivignesh</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). 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.</p>
</license>
</permissions>
<abstract>
<p>Drought stress is a prime abiotic constraint that reduces microgreen growth and nutritional quality. This research explores a new strategy involving using green-synthesized selenium nanoparticles (SeNPs) to improve drought stress tolerance and biofortification of Amaranthus microgreens (var. Arka Suguna). SeNPs were synthesized from <italic>Cassia auriculata</italic> leaf extract and characterized via UV-Vis spectroscopy, TEM, XRD, FT-IR, and DLS, establishing their crystalline nature, spherical shape (80.6&#x2013;135&#xa0;nm), and phytochemical capping. Toxicity screening indicated 1,000&#xa0;ppm as growth-inhibitory, whereas 100&#xa0;ppm was optimal for plant growth. Drought assays employing PEG-induced stress indicated that 100&#xa0;ppm SeNPs greatly enhanced germination (97.5%), yield (330&#xa0;mg), plant height (5.6&#xa0;cm), and biochemical profiles. Treated microgreens exhibited higher total protein (377.2&#xa0;mg/100&#xa0;g), carbohydrates (951&#xa0;mg/100&#xa0;g), flavonoids (11.4&#xa0;mg/g), vitamin C (36.67&#xa0;mg/100&#xa0;g), and antioxidant enzyme activities (SOD: 0.065&#xa0;U/mg/min; CAT: 13.5&#xa0;U/mg/min). SeNPs also promoted selenium accumulation (10.69&#xa0;mg/g DW) and had no negative impacts on valuable soil microbes, including <italic>Pseudomonas aeruginosa, Bacillus subtilis,</italic> and <italic>Trichoderma viride</italic>. This paper is the first comprehensive report on Cassia auriculata-mediated SeNPs administered through seed, soil, and foliar application to enhance drought tolerance and nutrient status in Amaranth microgreens. The findings indicate SeNPs as a green nano-priming approach for promoting crop yield under abiotic stress conditions.</p>
</abstract>
<abstract abstract-type="graphical">
<title>Graphical Abstract</title>
<p>
<graphic xlink:href="FNANO_fnano-2025-1621024_wc_abs.tif">
<alt-text content-type="machine-generated">Schematic showing the process of using green synthesized selenium nanoparticles (SeNPs) from Cassia auriculata. SeNPs are characterized using UV-Vis, TEM, XRD, and DLS techniques. Applications include seed priming, soil, and foliar application, enhancing drought resistance, plant height, and yield under PEG-induced drought conditions. Enhanced selenium content and soil microbe safety are noted. Caption: Green synthesized SeNP nano-priming boosts drought resilience, nutrition, and yield without harming soil health.</alt-text>
</graphic>
</p>
</abstract>
<kwd-group>
<kwd>selenium nanoparticles</kwd>
<kwd>amaranthus</kwd>
<kwd>microgreens</kwd>
<kwd>green synthesis</kwd>
<kwd>biofortification</kwd>
<kwd>sustainable agriculture</kwd>
<kwd>drought stress</kwd>
</kwd-group>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Environmental Nanotechnology</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1">
<title>1 Introduction</title>
<p>Selenium (Se), an essential micronutrient, exhibits potent antioxidant and antimicrobial properties, making it a cost-effective and safer option for agricultural and biomedical applications (<xref ref-type="bibr" rid="B1">Abbas et al., 2020</xref>). Compared to selenate or selenite, selenium nanoparticles (SeNPs) demonstrate lower toxicity while promoting plant growth, enhancing antioxidant activity, and improving vegetable nutrient accumulation (<xref ref-type="bibr" rid="B32">Hern&#xe1;ndez-Hern&#xe1;ndez et al., 2019</xref>). The antioxidant and anti-cancer potential of SeNPs is well-documented, but their synthesis method critically influences their safety and efficacy. Chemical synthesis using reducing agents like ascorbic acid often yields hazardous byproducts (<xref ref-type="bibr" rid="B41">Lin et al., 2021</xref>). In contrast, green synthesis utilizes plant extracts as reducing, stabilizing, and capping agents, offering an eco-friendly alternative that enhances SeNPs&#x2019; biocompatibility and functional properties (<xref ref-type="bibr" rid="B37">Kamal et al., 2019</xref>; <xref ref-type="bibr" rid="B7">Alsafran et al., 2025</xref>). This biogenic approach reduces toxicity and improves the antioxidant and anti-cancer effects of SeNPs without harming healthy cells (<xref ref-type="bibr" rid="B16">Budhani et al., 2019</xref>).</p>
<p>Nanotechnology has transformative applications across diverse sectors, including agriculture, where nanoparticles (1&#x2013;100&#xa0;nm) leverage unique physicochemical properties to enhance crop yields and sustainability (<xref ref-type="bibr" rid="B57">Usman et al., 2020</xref>). Innovations such as gold nanoparticles for COVID-19 antibody detection and 3D-printed nanomaterials underscore nanotechnology&#x2019;s versatility in medicine and materials science. In agriculture, nano-agrochemicals enable targeted delivery, controlled release, and improved solubility of nutrients, thereby minimizing environmental harm (<xref ref-type="bibr" rid="B6">Ali et al., 2018</xref>; <xref ref-type="bibr" rid="B18">Chhipa, 2019</xref>). Despite these advances, challenges like scalability and long-term ecological impacts require resolution (<xref ref-type="bibr" rid="B22">Du et al., 2023</xref>). Commonly used silver, titanium dioxide, Zinc oxide and silica nanoparticles have shown promise in boosting germination and stress resilience (<xref ref-type="bibr" rid="B53">Rastogi et al., 2019</xref>; <xref ref-type="bibr" rid="B28">Francis et al., 2024a</xref>). In addition, these metal nanoparticles enhance crop productivity (20% increase), stress tolerance, and nutrient efficiency while reducing disease (50%) and nutrient leaching (30%). However, risks like toxicity and environmental accumulation must be addressed for sustainable agricultural use (<xref ref-type="bibr" rid="B27">Francis et al., 2024b</xref>).</p>
<p>Microgreens, such as amaranth, are nutrient-dense crops valued for their high concentrations of secondary metabolites, minerals (Fe, Mg, K), and digestible proteins (<xref ref-type="bibr" rid="B10">Ayeni, 2021</xref>). However, abiotic stresses (e.g., drought, salinity) often limit their productivity, which triggers oxidative damage, impairing growth and metabolism (<xref ref-type="bibr" rid="B25">El-Saadony et al., 2022</xref>). Selenium nanoparticles (SeNPs) effectively counteract abiotic stress by modulating key physiological processes, including the upregulation of chlorophyll biosynthesis, enhancement of photosynthetic efficiency, and promotion of osmoprotectant accumulation (<xref ref-type="bibr" rid="B50">Rady et al., 2020</xref>). Furthermore, SeNPs stimulate the activity of critical antioxidant enzymes, such as ascorbate peroxidase (APX), superoxide dismutase (SOD), and catalase (CAT), which collectively mitigate oxidative damage through efficient scavenging of reactive oxygen species (ROS). This dual mechanism significantly bolsters plant stress adaptation and tolerance. The SeNPs, particularly biosynthesized ones, improve crops&#x2019; resilience to abiotic stresses (e.g., drought, salinity) by increasing germination, antioxidant activity, and stress-responsive genes. Their size and application method influence their efficacy in enhancing growth, photosynthesis, yield, and plant physiology (<xref ref-type="bibr" rid="B26">Fatima et al., 2024</xref>). Additionally, SeNPs exhibit antimicrobial activity by catalyzing the oxidation of intracellular thiols (<xref ref-type="bibr" rid="B59">Webster and Ramos, 2012</xref>). Earlier studies have shown that green-synthesized selenium nanoparticles (SeNPs) have been reported to act as biostimulants of the antioxidant defense and physiological processes. Recent study shows that the application of green-synthesized SeNPs in the alleviation of drought stress in numerous crops like Soyabean, Purple coneflower, Rice, and Wheat (<xref ref-type="bibr" rid="B61">Zeeshan et al., 2024</xref>; <xref ref-type="bibr" rid="B54">Rezagholi et al., 2025</xref>; <xref ref-type="bibr" rid="B34">Iqbal et al., 2025</xref>; <xref ref-type="bibr" rid="B24">El-Saadony et al., 2021</xref>). While numerous studies have investigated the potential of selenium nanoparticles (SeNPs) to alleviate abiotic stress in crops, most of these studies concentrate on conventional vegetables and field crops, frequently involving chemically synthesized particles.</p>
<p>The current study presents novel approaches, such as <italic>Cassia auriculata</italic> leaf extract, for the green synthesis of SeNPs, a less commonly investigated phytochemical source. Second, the research incorporates a combined application strategy, seed priming, soil drenching, and foliar spraying, which have not been thoroughly tested in microgreens under drought conditions. Third, we employed Amaranthus microgreens, a high-value crop with a short crop cycle characterized by nutritional density but underrepresented in SeNP research. Unlike previous reports, this study includes an in-depth characterization (UV-Vis, DLS, TEM, FT-IR, XRD), toxicity studies, and compatibility studies with beneficial soil microorganisms. Finally, our study provides a comprehensive assessment that includes growth, biochemical, enzymatic, and microbial compatibility parameters. It thus brings new information to the nano-enabled biofortification and stress tolerance area of short-cycle edible crops. By harnessing the synergistic potential of biogenic SeNPs and microgreens, this research aims to develop sustainable strategies for enhancing crop resilience in drought-stressed environments.</p>
</sec>
<sec sec-type="materials|methods" id="s2">
<title>2 Materials and methods</title>
<sec id="s2-1">
<title>2.1 Materials source</title>
<p>Sodium selenite (Na<sub>2</sub>SeO<sub>3</sub>) (MW of 172.94) was purchased from Hi Media, India. Fresh leaves of <italic>C. auriculata</italic> were collected from Tiruvannamalai district, Tamil Nadu, India (latitude 12.3841 and longitude 79.1178). The amaranthus variety used in the study is Arka Suguna, which is resourced from IIHR, Bangalore, India.</p>
</sec>
<sec id="s2-2">
<title>2.2 Biosynthesis of SeNPs</title>
<p>
<italic>Cassia auriculata</italic> leaf powder was tested at three concentrations (0.5, 2.5, and 5&#xa0;g) suspended in 100&#xa0;mL of double-distilled water (ddH<sub>2</sub>O) for optimal extract preparation. The suspensions were maintained in a water bath at 60&#xb0;C with continuous stirring (200&#xa0;rpm) for 30&#xa0;min. The resulting mixtures underwent sequential filtration: primary filtration through sterile muslin cloth to remove particulate matter, followed by vacuum filtration using Whatman No. 42 filter paper to eliminate residual macro particles. The clarified, particle-free extracts were aseptically transferred to sterile reagent bottles and stored at 4&#xb0;C for immediate use in SeNP synthesis. Sodium selenite (Na<sub>2</sub>SeO<sub>3</sub>; Molecular Weight: 172.94&#xa0;g/mol; HiMedia Laboratories) solutions were prepared in five concentrations (5, 8, 10, 12, and 15&#xa0;mM) using ddH<sub>2</sub>O as solvent. For SeNP synthesis, each concentration was combined with the standardized leaf extract (5&#xa0;g/100&#xa0;mL) in a 1:4 (v/v) ratio. The 1:4 ratio was chosen due to its demonstrated efficacy in prior optimization studies of NP production (<xref ref-type="bibr" rid="B38">Khurana et al., 2019</xref>; <xref ref-type="bibr" rid="B24">El-Saadony et al., 2021</xref>). The reaction mixtures were incubated at 75&#xb0;C (&#xb1;1&#xb0;C) for 25&#xa0;min in a hot plate magnetic stirrer (800&#xa0;rpm) to ensure complete reduction of Se<sup>4&#x2b;</sup> to Se<sup>0</sup>. Temperature and stirring speed were rigorously controlled to maintain consistent reaction kinetics across all trials.</p>
<p>To achieve optimal nanoparticle stability, the biosynthesized SeNP solution underwent controlled incubation in an orbital shaker (120&#xa0;rpm) under sequential temperature conditions: initial stabilization at 72&#xb0;C (&#xb1;0.5&#xb0;C) for 3&#xa0;h, followed by gradual cooling to 37&#xb0;C (&#xb1;0.5&#xb0;C) for extended incubation periods (6, 12, 24, 48, 60, and 72&#xa0;h). At each time interval, aliquots were aseptically collected and analyzed by UV-Vis spectroscopy to monitor plasmon resonance peak stability at 230&#xa0;nm. This dual-phase thermal protocol ensured progressive nanoparticle maturation while preventing aggregation.</p>
</sec>
<sec id="s2-3">
<title>2.3 Characterization of biosynthesized SeNPs</title>
<p>The synthesized biogenic selenium nanoparticle&#x2019;s physicochemical properties were characterized using advanced analytical techniques. UV-Vis spectral analysis was carried out on a Genesys 180 spectrophotometer (Thermo Fisher Scientific, United States), with absorbance measurements recorded across 200&#x2013;800&#xa0;nm wavelengths at 1&#xa0;nm intervals. Nanoparticle morphology and elemental composition were evaluated through transmission electron microscopy (Quanta 200 FEG, FEI, Netherlands) coupled with energy-dispersive X-ray spectroscopy (Oxford Instruments X-MaxN EDX system), performed at 200&#xa0;kV accelerating voltage at Tamil Nadu Agricultural University&#x2019;s facility. Crystalline structure was determined by X-ray diffraction analysis (Bruker D8 Advance, United States) employing a 2&#x3b8; range of 10&#xb0;&#x2013;80&#xb0; with 0.02&#xb0; step resolution. Surface functional group identification was achieved using FT-IR spectroscopy (PerkinElmer Spectrum Two) scanning the 4,000&#x2013;400&#xa0;cm<sup>&#x2212;1</sup> spectral range at Central University of Tamil Nadu&#x2019;s analytical laboratory. For quantitative analysis, TEM micrographs were processed using ImageJ software (v1.45, NIH) with threshold-based particle detection. Size distribution histograms and statistical parameters (mean &#xb1; SD) were generated using OriginPro 2022 (OriginLab Corporation) with Gaussian curve fitting. All measurements were performed in triplicates.</p>
</sec>
<sec id="s2-4">
<title>2.4 Biocompatibility assay and toxicity assay of biosynthesized SeNP</title>
<p>The biocompatibility of biosynthesized SeNPs was evaluated against two beneficial soil microorganisms: <italic>Bacillus subtilis</italic> (MTCC 121) and <italic>Pseudomonas aeruginosa</italic> (MTCC 7903). Sterile nutrient agar (20&#xa0;mL; HiMedia, M001) was supplemented with 5&#xa0;mL of SeNP solution (100&#xa0;ppm) in Petri plates (90&#xa0;mm diameter). Bacterial cultures (100&#xa0;&#xb5;L of 10<sup>8</sup>&#xa0;CFU/mL suspension) were spread-plated and incubated for 48&#xa0;h at 37&#xb0;C (&#xb1;0.2&#xb0;C). Microbial growth was assessed by measuring colony diameter (mm) and optical density (600&#xa0;nm) compared to untreated controls.</p>
<p>Seeds of Amaranthus var. Arka Suguna underwent surface sterilization using 0.4% (v/v) sodium hypochlorite solution for 5&#xa0;min, followed by three thorough rinses with sterile distilled water. After air-drying under aseptic conditions in a laminar flow hood, the sterilized seeds were transferred to Petri plates containing 2% plain agar media (HiMedia, GRM026), which had been pre-treated with either 100&#xa0;ppm SeNPs solution or control treatments. The plates were maintained in a growth chamber set at 25&#xb0;C with a 16-h photoperiod/8-h dark cycle. Daily observations were conducted over 7&#xa0;days to quantify germination percentage and measure radicle elongation (in mm).</p>
</sec>
<sec id="s2-5">
<title>2.5 Standardization of PEG concentration for artificial induction of drought</title>
<p>Artificial drought conditions were established using polyethylene glycol 6000 (PEG-6000; HiMedia, PCT1306). Four osmotic stress levels were tested: 16.7&#xa0;mM (&#x2212;0.05&#xa0;MPa), 25&#xa0;mM (&#x2212;0.10&#xa0;MPa), 37.5&#xa0;mM (&#x2212;0.20&#xa0;MPa), and 56.3&#xa0;mM (&#x2212;0.40&#xa0;MPa) PEG solutions. Each concentration was applied at 5&#xa0;mL per potray cell (4&#xa0;cm diameter &#xd7; 5&#xa0;cm depth) containing the growth medium. The optimal PEG concentration was determined based on germination percentage and Amaranthus var seedling vigor index. A standardized growth medium was prepared by homogenizing farmyard manure (FYM), river sand, and vermicompost in a 1:1:1 (v/v/v) ratio. Physical properties of the substrate were characterized (pH 6.8 &#xb1; 0.2, EC 1.2 &#xb1; 0.3&#xa0;dS/m).</p>
</sec>
<sec id="s2-6">
<title>2.6 Application methods of biosynthesized SeNPs</title>
<p>Surface-sterilized Amaranthus var. Arka Suguna seeds were nano-primed via incubation in 25 or 100&#xa0;ppm biosynthesized SeNP solutions (1:2 seed: solution ratio) for 60&#xa0;min at 25&#xa0;rpm (25&#xb0;C &#xb1; 1&#xb0;C) using a benchtop tube rotator before sowing. Soil application was performed on day 3 post-germination (D3) via root zone drenching with 100&#xa0;ppm SeNP solution (5&#xa0;mL/portray cell). In comparison, foliar spraying (25&#xa0;ppm, 1&#xa0;mL/portray cell) was conducted at the first true leaf stage (D6) using an atomizer (50&#x2013;100&#xa0;&#x3bc;m droplets) during peak stomatal activity to optimize uptake. All treatments were employed in controlled environmental conditions (28&#xb0;C &#xb1; 2&#xb0;C, 70% RH).</p>
</sec>
<sec id="s2-7">
<title>2.7 Determination of growth parameters</title>
<p>Amaranthus var. Arka Suguna microgreens were harvested at physiological maturity (9&#xa0;days post-sowing) for growth and yield evaluation. Germination percentage was calculated as (number of germinated seeds/total seeds sown) &#xd7; 100, with radicle emergence &#x2265;2&#xa0;mm as the germination criterion. Plant height was measured from the growth medium surface to the apical meristem using digital calipers (Mitutoyo, &#xb1;0.01&#xa0;mm precision). For yield analysis, fresh weight was recorded immediately post-harvest (Shimadzu balance, ATX224R, Japan), while dry weight measurements followed 48-h dehydration in a forced-air oven at 60&#xb0;C &#xb1; 1&#xb0;C (P-Lab, Precession lab industries, India) until constant mass was achieved. All measurements were conducted in triplicate across three independent experimental runs.</p>
</sec>
<sec id="s2-8">
<title>2.8 Determination of biochemical parameters</title>
<sec id="s2-8-1">
<title>2.8.1 Chlorophyll and carotenoid content</title>
<p>Chlorophyll and carotenoid content were analyzed using a modified acetone extraction method. Fresh leaf tissue (0.1&#xa0;g) was homogenized in 10&#xa0;mL of 80% acetone (HI-AR, AS025, Himedia laboratories, India) and then centrifuged at 5,000 &#xd7; g for 10&#xa0;min at 4&#xb0;C to separate debris. The absorbance of the supernatant was measured at 643&#xa0;nm and 660&#xa0;nm (GENESYS 180, Thermo Fisher Scientific) for chlorophyll quantification using established equations:<disp-formula id="equ1">
<mml:math id="m1">
<mml:mrow>
<mml:mtext>Chlorophyll&#x2009;</mml:mtext>
<mml:mi mathvariant="normal">a</mml:mi>
<mml:mo>&#x3d;</mml:mo>
<mml:mn>9.93</mml:mn>
<mml:mtext>&#x2009;</mml:mtext>
<mml:mrow>
<mml:mfenced open="(" close=")" separators="|">
<mml:mrow>
<mml:mi mathvariant="normal">A</mml:mi>
<mml:mn>660</mml:mn>
</mml:mrow>
</mml:mfenced>
</mml:mrow>
<mml:mo>&#x2212;</mml:mo>
<mml:mn>0.777</mml:mn>
<mml:mtext>&#x2009;</mml:mtext>
<mml:mrow>
<mml:mfenced open="(" close=")" separators="|">
<mml:mrow>
<mml:mi mathvariant="normal">A</mml:mi>
<mml:mn>643</mml:mn>
</mml:mrow>
</mml:mfenced>
</mml:mrow>
<mml:mo>&#xd7;</mml:mo>
<mml:mfrac>
<mml:mi mathvariant="normal">V</mml:mi>
<mml:mrow>
<mml:mi mathvariant="normal">W</mml:mi>
<mml:mo>&#xd7;</mml:mo>
<mml:mn>1000</mml:mn>
</mml:mrow>
</mml:mfrac>
</mml:mrow>
</mml:math>
</disp-formula>
<disp-formula id="equ2">
<mml:math id="m2">
<mml:mrow>
<mml:mtext>Chlorophyll&#x2009;</mml:mtext>
<mml:mi mathvariant="normal">b</mml:mi>
<mml:mo>&#x3d;</mml:mo>
<mml:mn>17.6</mml:mn>
<mml:mtext>&#x2009;</mml:mtext>
<mml:mrow>
<mml:mfenced open="(" close=")" separators="|">
<mml:mrow>
<mml:mi mathvariant="normal">A</mml:mi>
<mml:mn>643</mml:mn>
</mml:mrow>
</mml:mfenced>
</mml:mrow>
<mml:mo>&#x2212;</mml:mo>
<mml:mn>2.81</mml:mn>
<mml:mtext>&#x2009;</mml:mtext>
<mml:mrow>
<mml:mfenced open="(" close=")" separators="|">
<mml:mrow>
<mml:mi mathvariant="normal">A</mml:mi>
<mml:mn>660</mml:mn>
</mml:mrow>
</mml:mfenced>
</mml:mrow>
<mml:mo>&#xd7;</mml:mo>
<mml:mfrac>
<mml:mi mathvariant="normal">V</mml:mi>
<mml:mrow>
<mml:mi mathvariant="normal">W</mml:mi>
<mml:mo>&#xd7;</mml:mo>
<mml:mn>1000</mml:mn>
</mml:mrow>
</mml:mfrac>
</mml:mrow>
</mml:math>
</disp-formula>where V &#x3d; extract volume (mL) and W &#x3d; sample fresh weight (g).</p>
<p>The procedure proposed by <xref ref-type="bibr" rid="B47">Mazumdar and Majumder (2021)</xref> was employed to determine the carotenoid content with minor modifications. 10&#xa0;mL of 80% acetone was used to pulverize 0.1&#xa0;g of the plant sample. The extract was filtered and the volume was increased to 50&#xa0;mL using ddH2O. Using a spectrophotometer, the value was determined by measuring the carotenoid content at a specific wavelength (645, 660, and 663). The following formula was used to calculate the value:<disp-formula id="equ3">
<mml:math id="m3">
<mml:mrow>
<mml:mtext>Carotenoids&#x2009;</mml:mtext>
<mml:mrow>
<mml:mfenced open="(" close=")" separators="|">
<mml:mrow>
<mml:mtext>mg&#x2009;</mml:mtext>
<mml:msup>
<mml:mi>g</mml:mi>
<mml:mrow>
<mml:mo>&#x2212;</mml:mo>
<mml:mn>1</mml:mn>
</mml:mrow>
</mml:msup>
</mml:mrow>
</mml:mfenced>
</mml:mrow>
<mml:mo>&#x3d;</mml:mo>
<mml:mn>4.69</mml:mn>
<mml:mo>&#xd7;</mml:mo>
<mml:msub>
<mml:mi mathvariant="normal">A</mml:mi>
<mml:mn>660</mml:mn>
</mml:msub>
<mml:mo>&#x2212;</mml:mo>
<mml:mn>0.268</mml:mn>
<mml:mo>&#xd7;</mml:mo>
<mml:mn>20.2</mml:mn>
<mml:mtext>&#x2009;</mml:mtext>
<mml:mi mathvariant="normal">x</mml:mi>
<mml:mtext>&#x2009;</mml:mtext>
<mml:msub>
<mml:mi mathvariant="normal">A</mml:mi>
<mml:mn>645</mml:mn>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:mn>8.02</mml:mn>
<mml:mo>&#xd7;</mml:mo>
<mml:msub>
<mml:mi mathvariant="normal">A</mml:mi>
<mml:mn>663</mml:mn>
</mml:msub>
</mml:mrow>
</mml:math>
</disp-formula>
</p>
<p>All extractions were performed in triplicate under dim light to prevent pigment degradation.</p>
</sec>
<sec id="s2-8-2">
<title>2.8.2 Total soluble protein quantification</title>
<p>The soluble protein content was assessed using the Lowry method (<xref ref-type="bibr" rid="B43">Lowry et al., 1951</xref>), with modifications. Fresh plant tissue (0.1&#xa0;g) was homogenized in 5&#xa0;mL of ice-cold phosphate buffer (0.1&#xa0;M, pH 7.0) and subsequently centrifuged at 10,000 &#xd7; g for 15&#xa0;min at 4&#xb0;C. One milliliter of supernatant was mixed with 5&#xa0;mL of alkaline copper reagent and incubated at 25&#xb0;C &#xb1; 1&#xb0;C for a duration of 10&#xa0;min. Following the addition of 0.5&#xa0;mL of Folin-Ciocalteu reagent (1:1 dilution), absorbance was assessed at 660&#xa0;nm utilizing a UV-VIS Spectrophotometer (GENESYS 180), with a phosphate buffer blank serving as the reference. Protein concentration was assessed using a bovine serum albumin (BSA) standard curve with a range of 0&#x2013;100&#xa0;&#x3bc;g/mL.</p>
</sec>
<sec id="s2-8-3">
<title>2.8.3 Total carbohydrate estimation</title>
<p>Carbohydrate content was analyzed via the anthrone-sulfuric acid method. Lyophilized samples (50&#xa0;mg) were hydrolyzed with 1.25&#xa0;mL 2.5&#xa0;N HCl at 100&#xb0;C for 3&#xa0;hours, neutralized with sodium carbonate and diluted to 50&#xa0;mL with ddH2O. After centrifugation (1,000 &#xd7; g, 10&#xa0;min), aliquots (1&#xa0;mL) were reacted with 4&#xa0;mL ice-cold anthrone reagent at 100&#xb0;C for 8&#xa0;min. The green-to-dark green color transition was quantified at 630&#xa0;nm using a UV-VIS Spectrophotometer. All extractions and reactions were performed in triplicate.</p>
</sec>
<sec id="s2-8-4">
<title>2.8.4 Total phenolic content</title>
<p>Phenolic compounds in fresh leaf samples were quantified using the Folin-Ciocalteu assay. Methanolic extracts (0.5&#xa0;mL, 70% v/v) were mixed with 0.2&#xa0;mL&#xa0;F-C reagent (1N), 3.25&#xa0;mL ddH<sub>2</sub>O, and 1&#xa0;mL 20% (w/v) Na<sub>2</sub>CO<sub>3</sub>. After vortexing (30&#xa0;s), samples were incubated in amber vials (25&#xb0;C &#xb1; 1&#xb0;C, 30&#xa0;min) to develop the chromogenic reaction. The absorbance at 700&#xa0;nm was compared to a methanol blank using a UV-VIS Spectrophotometer. The calibration curve (Y &#x3d; 0.012X &#x2b; 0.021; R<sup>2</sup> &#x3d; 0.998) was generated by gallic acid standards (0&#x2013;100&#xa0;&#x3bc;g/mL), and the results were expressed as mg gallic acid equivalents (GAE) per g fresh weight.</p>
</sec>
<sec id="s2-8-5">
<title>2.8.5 Total flavonoid content</title>
<p>Flavonoids were analyzed via aluminum chloride complexation (<xref ref-type="bibr" rid="B66">Ordonez et al., 2006</xref>). Methanolic extracts (1&#xa0;mL) were combined with 1.5&#xa0;mL 80% methanol, 0.1&#xa0;mL 10% (w/v) AlCl<sub>3</sub>, 0.1&#xa0;mL 1M CH<sub>3</sub>COONa, and 2.8&#xa0;mL ddH<sub>2</sub>O. Following incubation (25&#xb0;C, 30&#xa0;min, dark), absorbance at 415&#xa0;nm was compared against quercetin standards (0&#x2013;50&#xa0;&#x3bc;g/mL; Y &#x3d; 0.025X&#x2013;0.112; R<sup>2</sup> &#x3d; 0.991). Data were expressed as mg quercetin equivalents (QE) per g fresh weight.</p>
</sec>
<sec id="s2-8-6">
<title>2.8.6 FRAP assay</title>
<p>Total antioxidant activity was assessed using the FRAP protocol by <xref ref-type="bibr" rid="B13">Benzie and Strain (1999)</xref>. The working solution consisted of 10&#xa0;mL of 300&#xa0;mM acidified acetate buffer, 1&#xa0;mL of 10&#xa0;mM TPTZ in hydrochloric acid, and 1&#xa0;mL of 20&#xa0;mM ferric chloride. Plant extracts (0.5&#xa0;mL) were mixed with 1.8&#xa0;mL of the FRAP reagent and 1.2&#xa0;mL of ultrapure water, then incubated at room temperature for 30&#xa0;min. Absorbance at 593&#xa0;nm was measured spectrophotometrically and converted to antioxidant equivalents using a calibration curve based on ascorbic acid standards, showing good linearity (r<sup>2</sup> &#x3d; 0.964). Antioxidant capacity was normalized to sample mass and expressed as micromolar ascorbic acid equivalents per gram of fresh tissue weight (&#x3bc;mol AAE/g FW).</p>
</sec>
<sec id="s2-8-7">
<title>2.8.7 Total soluble sugars</title>
<p>Glucose content (% w/w) and total soluble solids (TSS, % Brix) were quantified using digital refractometry. Fresh tissue (1&#xa0;g) was homogenized in 10&#xa0;mL ddH<sub>2</sub>O (1:10 w/v) and filtered through a muslin cloth. Clear extracts were analyzed using calibrated digital meters: glucose (HI96803, HANNA range 0%&#x2013;85%) and TSS (HI96801, HANNA, range 0&#x2013;85&#xb0;Brix). Results represent the mean of three technical replicates per biological sample.</p>
</sec>
<sec id="s2-8-8">
<title>2.8.8 Vitamin C quantification</title>
<p>L-ascorbic acid was measured via redox titration (<xref ref-type="bibr" rid="B20">Contreras-Calder&#xf3;n et al., 2010</xref>). Samples (0.05&#xa0;g) were homogenized in 10&#xa0;mL 4% (w/v) oxalic acid and centrifuged (8,000 &#xd7; g, 10&#xa0;min). The supernatant (5&#xa0;mL) was titrated against standardized 2,6-dichlorophenolindophenol (DCPI, 0.1&#xa0;mg/mL) until a persistent pink endpoint (pH 3.0&#x2013;4.0). Vitamin C content (mg/100&#xa0;g FW) was calculated.</p>
</sec>
</sec>
<sec id="s2-9">
<title>2.9 Antioxidant enzymatic activities</title>
<sec id="s2-9-1">
<title>2.9.1 Superoxide dismutase (SOD) activity assay</title>
<p>The superoxide dismutase (SOD; EC 1.15.1.1) enzymatic assay was performed according to established photochemical methods (<xref ref-type="bibr" rid="B14">Beyer and Fridovich, 1987</xref>). Plant tissue samples were homogenized in 50&#xa0;mM phosphate buffer (pH 7.8) containing 1% (w/v) polyvinylpyrrolidone to minimize phenolic compound interference. The complete reaction system (4&#xa0;mL final volume) incorporated 50&#xa0;mM phosphate buffer (pH 7.8), 0.15&#xa0;mM EDTA, 0.12&#xa0;mM NBT, 20&#xa0;mM methionine, and 0.075&#xa0;mM riboflavin. Following addition of 500&#xa0;&#x3bc;L enzyme extract, the mixture was exposed to 5,000 lux fluorescent illumination for 30&#xa0;min to generate superoxide radicals and initiate NBT reduction. Absorbance measurements at 560&#xa0;nm determined the extent of reaction inhibition, with one SOD unit defined as the enzyme quantity required for 50% suppression of NBT reduction compared to light-exposed controls. Activity calculations employed the formula: % inhibition &#x3d; [(A560 control - A560 sample)/A560 control] &#xd7; 100. All experimental measurements included triplicate analyses along with appropriate light-exposed and dark control samples to ensure methodological reliability.</p>
</sec>
<sec id="s2-9-2">
<title>2.9.2 Catalase assay</title>
<p>The enzymatic activity of catalase (EC 1.11.1.6) was quantified using UV-visible spectrophotometry based on hydrogen peroxide decomposition kinetics. Following the established protocol of <xref ref-type="bibr" rid="B4">Aebi (1984)</xref>, enzyme extraction was performed in ice-cold 50&#xa0;mM phosphate buffer (pH 7.0), with subsequent clarification through centrifugation (10,000 &#xd7; g, 15&#xa0;min, 4&#xb0;C). The assay system consisted of 3&#xa0;mL reaction volume containing: (1) 50&#xa0;mM phosphate buffer (pH 7.0), (2) 10&#xa0;mM H<sub>2</sub>O<sub>2</sub> substrate solution, and (3) 100&#xa0;&#x3bc;L of enzyme extract. Catalase-mediated H<sub>2</sub>O<sub>2</sub> breakdown was monitored by measuring absorbance decline at 240&#xa0;nm (extinction coefficient &#x3d; 39.4&#xa0;mM<sup>&#x2212;1</sup>cm<sup>&#x2212;1</sup>) for 60&#xa0;s at 25&#xb0;C. Enzyme activity calculations were normalized to total protein content and reported as micromoles of H<sub>2</sub>O<sub>2</sub> catabolized per minute per milligram of protein.</p>
</sec>
</sec>
<sec id="s2-10">
<title>2.10 Estimation of selenium content</title>
<p>Selenium concentration in Amaranthus microgreens was determined using a modified (<xref ref-type="bibr" rid="B64">Duff and Chessin, 1965</xref>) acid digestion method. 0.5&#xa0;g of tissue was digested in a 10&#xa0;mL acid mixture (7.5:2.5 v/v nitric: perchloric acids) at 85&#xb0;C&#x2013;100&#xb0;C until white fumes appeared. After cooling, 3&#xa0;mL 30% hydrogen peroxide (H2O2) was added and reheated (5&#x2013;10&#xa0;min) to complete oxidation. The digestate was reacted with 10&#xa0;mL 3% hydrazine sulfate (reducing agent) and 3&#xa0;mL 2.5% gum arabic (stabilizer) in a boiling water bath (10&#xa0;min), producing an orange-red Se-hydrazine complex. The final volume was adjusted to 25&#xa0;mL using deionized water, and absorbance was recorded at 420&#xa0;nm relative to sodium selenite standards (0&#x2013;5&#xa0;ppm). Spike recovery tests (90%&#x2013;105%) and reagent blanks validated the protocol, with results expressed as mg Se/g dry weight (triplicate measurements).</p>
</sec>
<sec id="s2-11">
<title>2.11 Statistical analysis</title>
<p>Three independent biological replicates were performed for all experimental treatments. Data analysis was conducted using R Statistical Software (version 4.2.3) with specialized packages for agricultural research (dplyr v1.1.0, agricolae v1.3-6, and multicomp v1.4-23). Treatment comparisons were assessed through one-way analysis of variance (ANOVA) followed by <italic>post hoc</italic> testing using Tukey&#x2019;s honestly significant difference (HSD) method at &#x3b1; &#x3d; 0.05. Significant differences between treatment groups were indicated using compact letter display notation following standard agricultural research conventions. For additional verification, Fisher&#x2019;s least significant difference (LSD) test was performed at the 5% probability level. All graphical representations were generated using GraphPad Prism software (version 8.4.3) to visualize treatment effects and statistical relationships.</p>
</sec>
</sec>
<sec id="s3">
<title>3 Result and discussion</title>
<sec id="s3-1">
<title>3.1 Standardization of leaf extract, sodium selenite concentrations and incubation time for the biosynthesis of SeNP</title>
<p>The biosynthesis of selenium nanoparticles (SeNPs) was optimized using <italic>C. auriculata</italic> leaf extract with various concentrations of sodium selenite (5&#xa0;mM, 8&#xa0;mM, 10&#xa0;mM, 12&#xa0;mM, 15&#xa0;mM) and incubation hours (6, 12, 24, 48, 60, 72&#xa0;h). Among tested concentrations, 5% leaf extract combined with 12&#xa0;mM sodium selenite yielded the most effective SeNP synthesis, exhibiting peak absorbance at 230&#xa0;nm with high intensity (<xref ref-type="fig" rid="F1">Figure 1A</xref>). The reduction process commenced immediately upon mixing. Subsequent stabilization studies revealed that a 72-h incubation period at 120&#xa0;rpm produced SeNPs with the highest absorbance peak (<xref ref-type="fig" rid="F1">Figure 1B</xref>). These standardized conditions 5% leaf extract, 12&#xa0;mM sodium selenite, and 72-h incubation were thus established as optimal for efficient and stable SeNP biosynthesis.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>Variations in the absorption spectra of <bold>(A)</bold> Sodium selenite with increasing concentrations (5&#xa0;mM, 8&#xa0;nM, 10&#xa0;nM, 12&#xa0;nM, 15&#xa0;nM), <bold>(B)</bold> Incubation time for SeNP reduction (6, 12, 24, 36, 48, 60, 72&#xa0;h).</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g001.tif">
<alt-text content-type="machine-generated">Graph A displays absorption curves at concentrations from five millimolar to fifteen millimolar, peaking around 230 nanometers. Graph B shows absorption curves over time from six to seventy-two hours, also peaking near 230 nanometers. Both graphs indicate variations in absorption intensity with changes in concentration and time.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s3-2">
<title>3.2 Standardization of PEG concentration for artificial induction of drought</title>
<p>To establish an effective <italic>in vitro</italic> drought induction system, polyethylene glycol (PEG) was tested at varying concentrations (16.7, 25, 37.5, 56.3&#xa0;mM). Results demonstrated that 37.5&#xa0;mM and 56.3&#xa0;mM PEG most effectively simulated drought stress (<xref ref-type="fig" rid="F2">Figure 2</xref>), as evidenced by pronounced physiological responses. Thus, 37.5&#xa0;mM PEG concentration was selected for subsequent experiments to evaluate drought-induced changes in plant biochemical and physiological parameters.</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>Standardization of PEG concentrations (16.7, 25, 37.5, 56.3&#xa0;mM) for artificial drought induction in Amaranth microgreens var. Arka Suguna.</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g002.tif">
<alt-text content-type="machine-generated">Five panels showing plant growth in different concentrations of a solution. The first panel labeled &#x22;Control&#x22; shows healthy plant growth. Subsequent panels labeled 16.7 mM, 25 mM, 37.5 mM, and 56.3 mM show progressively reduced plant growth, with the highest concentration showing minimal or no growth.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s3-3">
<title>3.3 Biocompatibility of biosynthesized SeNP with beneficial microorganisms and toxicity test</title>
<p>The biocompatibility assessment of biosynthesized SeNPs (100&#xa0;ppm) demonstrated a stimulatory effect on beneficial soil microorganisms, including <italic>P. aeruginosa</italic> and <italic>B. subtilis</italic>. Unlike exhibiting inhibitory effects, the SeNPs enhanced microbial growth compared to untreated controls (<xref ref-type="fig" rid="F3">Figures 3A,B</xref>). These findings suggest that the biosynthesized SeNPs maintain compatibility with essential soil microbiota while potentially promoting their proliferation. A toxicity assessment of biosynthesized SeNPs was conducted on Amaranthus var. Arka Suguna microgreens using four concentrations (100, 250, 500 and 1,000&#xa0;ppm). While the highest concentration (1,000&#xa0;ppm) exhibited phytotoxic effects, impairing plant development, lower concentrations (100&#x2013;500&#xa0;ppm) showed no adverse effects and instead promoted normal growth (<xref ref-type="fig" rid="F3">Figure 3C</xref>). These results establish a concentration-dependent response to SeNPs, with 1,000&#xa0;ppm representing the toxicity threshold for this cultivar.</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>Biocompatibility of biosynthesized SeNPs with beneficial microorganisms <bold>(A)</bold> <italic>Bacillus subtilis</italic>, <bold>(B)</bold> <italic>Pseudomonas aeruginosa</italic> and <bold>(C)</bold> Effects of SeNPs on toxicity levels of <italic>Invitro</italic> germinated Amaranthus seeds.</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g003.tif">
<alt-text content-type="machine-generated">Petri dish experiment with bacterial cultures. Panel A shows Bacillus subtilis with growth restriction in one dish. Panel B shows Pseudomonas aeruginosa with similar restriction. Panel C displays a control dish and dishes with varying concentrations (100 ppm to 1000 ppm) showing decreasing bacterial growth.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s3-4">
<title>3.4 Characterization of biosynthesized SeNPs</title>
<p>UV-Vis spectroscopic analysis of biosynthesized SeNPs (prepared with 12&#xa0;mM sodium selenite and 5% C. auriculata leaf extract) revealed characteristic absorbance peaks at 230&#xa0;nm for all tested samples, including 100&#xa0;ppm SeNPs, pure selenium powder, and crude leaf extract (<xref ref-type="fig" rid="F4">Figure 4A</xref>). Dynamic light scattering analysis indicated the synthesized nanoparticles had an average size distribution of 337.3&#xa0;nm with a polydispersity index (PdI) of 0.321 (<xref ref-type="fig" rid="F4">Figure 4B</xref>), demonstrating moderate size variation among the nanoparticles. The particle size measurements, polydispersity index (PDI), and zeta potential were carried out in Milli-Q water as the dispersion medium. Nevertheless, it is established that such physicochemical features are highly affected by the matrix surrounding it, e.g., ionic strength, pH, and the occurrence of macromolecules like root exudates and soil colloids (<xref ref-type="bibr" rid="B24">El-Saadony et al., 2021</xref>; <xref ref-type="bibr" rid="B34">Iqbal et al., 2025</xref>). Thus, under real application conditions like seed coating, soil correction, or foliar spraying, nanoparticle behavior can differ significantly from that seen in water. Environmental interactions may influence nanoparticle stability, uptake efficiency, and biological efficacy. Future studies should consider evaluating nanoparticles&#x2019; size distribution and surface charge directly in the relevant matrices to better correlate their physicochemical properties with plant responses and agronomic outcomes.</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>
<bold>(A)</bold> UV-visible spectrums after 72&#xa0;h of incubation of crude extract of biosynthesized SeNPs, pure sodium selenite powder 99%, biosynthesized SeNPs (100&#xa0;ppm)- sterilized, biosynthesized SeNPs (100&#xa0;ppm)- non sterilized; <bold>(B)</bold> dynamic light scattering pattern of biosynthesized SeNPs; <bold>(C)</bold> Fourier transform intra-red spectroscopy (FTIR) spectra of - Cassia auriculata leaf extract, <bold>(D)</bold> sodium selenite, <bold>(E)</bold> biosynthesized SeNPs; <bold>(F)</bold> X-ray diffraction pattern of - chemically synthesized SeNPs (ascorbic acid as reducer), <bold>(G)</bold> biosynthesized SeNPs (C. auriculata extract as reducer).</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g004.tif">
<alt-text content-type="machine-generated">Panel of graphs depicting various analyses of selenium nanoparticles (SeNPs): A) UV-Vis absorption spectra showing different samples including crude extract and biosynthesized SeNPs. B) Size distribution by intensity indicating nanoparticle size. C, D, E) FTIR spectra showing functional groups present. F) XRD pattern showing crystalline phases. G) XRD pattern with different intensity scale. These graphs collectively depict characterization results for SeNPs.</alt-text>
</graphic>
</fig>
<p>FT-IR spectroscopy confirmed the involvement of functional groups from <italic>C. auriculata</italic> leaf extract in the reduction and stabilization of biosynthesized SeNPs. Comparative analysis of the leaf extract (<xref ref-type="fig" rid="F4">Figure 4C</xref>), sodium selenate (<xref ref-type="fig" rid="F4">Figure 4D</xref>), and biosynthesized SeNPs (<xref ref-type="fig" rid="F4">Figure 4E</xref>) identified key vibrational frequencies, including a broad OH stretch at 3291.09&#xa0;cm<sup>&#x2212;1</sup> (indicative of aromatic rings and ether-methoxy groups) and C&#x2013;H asymmetric bending at 1066.03&#xa0;cm<sup>&#x2212;1</sup> and 92.99&#xa0;cm<sup>&#x2212;1</sup>. The observed redshift in the OH band of SeNPs suggested hydroxyl group interactions with nanoparticle surfaces, a critical factor in their stabilization. Spectral changes, including the retention or disappearance of&#x2013;OH/COO&#x2013;peaks, further supported the role of these functional groups in capping and stabilizing the SeNPs. These findings align with reported mechanisms of plant-mediated nanoparticle synthesis and stabilization. The X-ray diffraction (XRD) result reveals that the biosynthesized SeNPs are amorphous in nature (<xref ref-type="fig" rid="F4">Figures 4F, G</xref>). The result matches with the previous reported values (<xref ref-type="bibr" rid="B17">Chen et al., 2009</xref>).</p>
<p>TEM analysis revealed spherical selenium nanoparticles (SeNPs) with distinct size distributions: chemically synthesized SeNPs ranged from 100 to 200&#xa0;nm (<xref ref-type="fig" rid="F5">Figure 5A</xref>), while biosynthesized SeNPs using <italic>C. auriculata</italic> leaf extract exhibited smaller sizes (80.6&#x2013;135&#xa0;nm; <xref ref-type="fig" rid="F5">Figures 5B,C</xref>). EDAX confirmed Se presence in all samples, with characteristic absorption peaks at 0.1&#x2013;0.5&#xa0;keV and 10&#x2013;10.5&#xa0;keV (<xref ref-type="fig" rid="F5">Figures 5D&#x2013;F</xref>). The 5&#xa0;mM Na<sub>2</sub>SeO<sub>3</sub>-derived SeNPs showed higher peak intensity in the lower energy range than 12&#xa0;mM Na<sub>2</sub>SeO<sub>3</sub> or ascorbic acid-synthesized particles. Size distribution analysis further demonstrated that ascorbic acid-produced SeNPs had the largest mean area (953.7&#xa0;nm<sup>2</sup>) and particle size (163.71&#xa0;nm). At the same time, biosynthesized SeNPs (5&#xa0;mM and 12&#xa0;mM Na<sub>2</sub>SeO<sub>3</sub>) displayed smaller, more uniform dimensions (<xref ref-type="fig" rid="F5">Figures 5G&#x2013;L</xref>). Copper signals in EDAX spectra originated from the TEM grid substrate.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption>
<p>
<bold>(A)</bold> TEM image of synthesized SeNP using Ascorbic acid as a reducer. <bold>(B)</bold> TEM image of synthesized SeNP using 5 mM Na<sub>2</sub>Se<sub>2</sub>O<sub>3</sub>. <bold>(C)</bold> TEM image of synthesized SeNP using 12 mM Na<sub>2</sub>Se<sub>2</sub>O<sub>3</sub>. <bold>(D)</bold> EDAX profile of synthesized SeNP using Ascorbic acid as a reducer. <bold>(E)</bold> EDAX profile of synthesized SeNP using 5 mM Na<sub>2</sub>Se<sub>2</sub>O<sub>3</sub>. <bold>(F)</bold> EDAX profile of synthesized SeNP using 12 mM Na<sub>2</sub>Se<sub>2</sub>O<sub>3</sub>. <bold>(G)</bold> Area distribution (nm<sup>2</sup>) of synthesized SeNP using Ascorbic acid as a reducer. <bold>(H)</bold> Area distribution (nm<sup>2</sup>) of synthesized SeNP using 5 mM Na<sub>2</sub>Se<sub>2</sub>O<sub>3</sub>. <bold>(I)</bold> Area distribution (nm<sup>2</sup>) of synthesized SeNP using 12 mM Na<sub>2</sub>Se<sub>2</sub>O<sub>3</sub>. <bold>(J)</bold> Size distribution (nm) of synthesized SeNP using Ascorbic acid as a reducer. <bold>(K)</bold> Size distribution(nm) of synthesized SeNP using 5 mM Na<sub>2</sub>Se<sub>2</sub>O<sub>3</sub>. <bold>(L)</bold> Size distribution(nm) of synthesized SeNP using 12 mM Na<sub>2</sub>Se<sub>2</sub>O<sub>3</sub>.</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g005.tif">
<alt-text content-type="machine-generated">TEM images labeled A, B, C show nanoparticles with varying sizes. Corresponding Edax profiles D, E, F indicate elemental composition with highlighted peaks. Graphs G, H, I present area distributions of nanoparticles, while J, K, L show size distributions. Columns represent different conditions: ascorbic acid as reducer, 5 millimolar sodium selenite, and 12 millimolar sodium selenite.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s3-5">
<title>3.5 Effect of SeNP on amaranthus growth and yield parameters</title>
<p>Se is generally considered a non-essential micronutrient for the plant growth (<xref ref-type="bibr" rid="B62">Zhan et al., 2021</xref>). Recent studies highlighted the potential of SeNp to improve germination percentage, growth and stress tolerance in various crops (<xref ref-type="bibr" rid="B3">Abouelhamd et al., 2023</xref>; <xref ref-type="bibr" rid="B29">Ghanbari et al., 2023</xref>). The study investigated the effects of biogenic synthesized SeNp on the growth attributes of amaranth microgreens (Amaranthus var Arka Suguna) under artificially induced drought conditions with PEG @ 37.5&#xa0;mM). The combined application method involves seed treatment (ST) and soil application of SeNp at 100&#xa0;ppm conc. (SA) and foliar application at 25&#xa0;ppm conc. (FA) had a significant impact on all growth parameters. The combined application (ST&#x2b;SA&#x2b;FA) enhanced seed germination to 96.67% under artificial drought stress while also increasing plant height (5.63&#xa0;cm), fresh weight (332.24&#xa0;mg) and dry weight (24.14&#xa0;mg) of harvested amaranth microgreens (<xref ref-type="table" rid="T1">Table 1</xref>; <xref ref-type="fig" rid="F6">Figure 6</xref>). The seed treatment combined with the soil application (ST&#x2b;SA) followed the ST&#x2b;SA&#x2b;FA treatment in terms of germination percentage, and plant height, showing similar results. However, the ST&#x2b;SA treatment did not significantly differ in fresh weight (283.87&#xa0;mg) and dry weight (23.93&#xa0;mg) compared to the combined application. The lowest germination percentage of 72.50 percent, plant height of 4.43&#xa0;cm, fresh weight 205.48, and dry weight 14.91&#xa0;mg was observed in control (<xref ref-type="fig" rid="F6">Figure 6</xref>). The findings of this study align with previous research indicated that biosynthesized SeNPS significantly increases the germination percentage of Amaranth microgreens. Similar growth promotion by SeNp has been reported in carrot plants (<xref ref-type="bibr" rid="B3">Abouelhamd et al., 2023</xref>), green beans (<xref ref-type="bibr" rid="B35">Ismail et al., 2023</xref>), and potatoes (<xref ref-type="bibr" rid="B49">Perfileva et al., 2023</xref>) increased plant height and physiological tolerance (<xref ref-type="bibr" rid="B65">Nagdalian et al., 2023</xref>). reported that applying SeNp at 20&#xa0;mg/L concentration enhances the growth in barley. These results support the role of SeNp in enhancing plant growth under stress conditions (<xref ref-type="fig" rid="F6">Figures 6A&#x2013;D</xref>).</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Effect of SeNPs on growth and yield parameters of Amaranth microgreens var. Arka Suguna in <italic>In-vivo</italic>.</p>
</caption>
<table>
<thead valign="top">
<tr style="background-color:#D9D9D9">
<th align="center">Treatments</th>
<th align="center">Germination percentage (%)</th>
<th align="center">Plant height (cm)</th>
<th align="center">Fresh weight (mg)</th>
<th align="center">Dry weight (mg)</th>
<th align="center">Chlorophyll A (mg/100&#xa0;g)</th>
<th align="center">Chlorophyll B (mg/100&#xa0;g)</th>
<th align="center">Carotenoid (mg/g)</th>
<th align="center">TSS (<sup>O</sup>Brix)</th>
<th align="center">Glucose (%W/W)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Control</td>
<td align="left">72.50 &#xb1; 2.5<sup>c</sup>
</td>
<td align="left">4.43 &#xb1; 0.06<sup>d</sup>
</td>
<td align="left">205.48 &#xb1; 1.50<sup>e</sup>
</td>
<td align="left">14.91 &#xb1; 2.08<sup>c</sup>
</td>
<td align="left">0.69 &#xb1; 0.02<sup>b</sup>
</td>
<td align="left">0.17 &#xb1; 0.005<sup>b</sup>
</td>
<td align="left">57.2 &#xb1; 6.23<sup>b</sup>
</td>
<td align="left">0.77 &#xb1; 0.15<sup>b</sup>
</td>
<td align="left">0.52 &#xb1; 0.01<sup>e</sup>
</td>
</tr>
<tr>
<td align="left">ST</td>
<td align="left">92.50 &#xb1; 2.5<sup>b</sup>
</td>
<td align="left">5.23 &#xb1; 0.06<sup>b</sup>
</td>
<td align="left">245.01 &#xb1; 0.88<sup>d</sup>
</td>
<td align="left">17.10 &#xb1; 2.09<sup>c</sup>
</td>
<td align="left">0.76 &#xb1; 0.07<sup>b</sup>
</td>
<td align="left">0.17 &#xb1; 0.02<sup>b</sup>
</td>
<td align="left">60.4 &#xb1; 3.73<sup>b</sup>
</td>
<td align="left">0.80 &#xb1; 0.10<sup>a</sup>
</td>
<td align="left">0.63 &#xb1; 0.00<sup>d</sup>
</td>
</tr>
<tr>
<td align="left">ST&#x2b;SA</td>
<td align="left">96.67 &#xb1; 2.5<sup>a</sup>
</td>
<td align="left">5.63 &#xb1; 0.06<sup>a</sup>
</td>
<td align="left">314.61 &#xb1; 10.4<sup>b</sup>
</td>
<td align="left">25.09 &#xb1; 2.35<sup>ab</sup>
</td>
<td align="left">0.84 &#xb1; 0.09<sup>ab</sup>
</td>
<td align="left">0.19 &#xb1; 0.01<sup>ab</sup>
</td>
<td align="left">63.4 &#xb1; 2.42<sup>b</sup>
</td>
<td align="left">1.33 &#xb1; 0.20<sup>a</sup>
</td>
<td align="left">1.47 &#xb1; 0.05<sup>b</sup>
</td>
</tr>
<tr>
<td align="left">ST&#x2b;FA</td>
<td align="left">92.50 &#xb1; 1.4<sup>b</sup>
</td>
<td align="left">5.10 &#xb1; 0.10<sup>c</sup>
</td>
<td align="left">283.87 &#xb1; 4.62<sup>c</sup>
</td>
<td align="left">23.93 &#xb1; 1.07<sup>b</sup>
</td>
<td align="left">0.78 &#xb1; 0.05<sup>b</sup>
</td>
<td align="left">0.18 &#xb1; 0.01<sup>b</sup>
</td>
<td align="left">63.1 &#xb1; 7.25<sup>b</sup>
</td>
<td align="left">1.20 &#xb1; 0.10<sup>a</sup>
</td>
<td align="left">1.03 &#xb1; 0.02<sup>c</sup>
</td>
</tr>
<tr>
<td align="left">ST&#x2b;SA&#x2b;FA</td>
<td align="left">96.67 &#xb1; 1.4<sup>a</sup>
</td>
<td align="left">5.63 &#xb1; 0.06<sup>a</sup>
</td>
<td align="left">332.24 &#xb1; 1.79<sup>a</sup>
</td>
<td align="left">28.14 &#xb1; 2.38<sup>a</sup>
</td>
<td align="left">1.03 &#xb1; 0.23<sup>a</sup>
</td>
<td align="left">0.24 &#xb1; 0.06<sup>a</sup>
</td>
<td align="left">79.7 &#xb1; 16.9<sup>a</sup>
</td>
<td align="left">1.30 &#xb1; 0.26<sup>a</sup>
</td>
<td align="left">2.13 &#xb1; 0.05<sup>a</sup>
</td>
</tr>
<tr>
<td align="left">CD (p &#x2264; 0.05)</td>
<td align="left">3.89</td>
<td align="left">0.12</td>
<td align="left">9.49</td>
<td align="left">3.72</td>
<td align="left">0.21</td>
<td align="left">0.05</td>
<td align="left">16.19</td>
<td align="left">0.32</td>
<td align="left">0.06</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Control- No Nanoparticles applied, ST: Seed treatment with SeNPs (100&#xa0;ppm), ST &#x2b; SA: Seed treatment with SeNPs (100&#xa0;ppm) and Soil application with SeNPs (100&#xa0;ppm), ST &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm), ST &#x2b; SA &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm), Soil application with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm). Data presented in the table represents the mean &#xb1; SD (n &#x3d; 3) at the significance level of p &#x2264; 0.05.</p>
</fn>
<fn>
<p>
<sup>a-d</sup>represents the statistical significance among the treatments. Treatments with same letters are statically on-par with each other.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption>
<p>Effects of SeNPs and drought stress on <bold>(A)</bold> Germination Percentage, <bold>(B)</bold> Plant height, <bold>(C)</bold> shoot fresh weight, <bold>(D)</bold> shoot dry weight in Amaranth microgreens var. Arka Suguna. All the plants were drought-stressed with PEG (37.5&#xa0;mM). Control- No Nanoparticles applied, ST: Seed treatment with SeNPs (100&#xa0;ppm), ST &#x2b; SA: Seed treatment with SeNPs (100&#xa0;ppm) and Soil application with SeNPs (100&#xa0;ppm), ST &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm), ST &#x2b; SA &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm), Soil application with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm). Different letters demonstrate significant differences among the treatments (p &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g006.tif">
<alt-text content-type="machine-generated">Bar graphs labeled A to D compare the effects of different treatments on plant growth metrics: germination percentage, plant height, fresh weight, and dry weight. Treatments include Control, ST, ST+SA, ST+FA, and ST+SA+FA. Each bar is color-coded with Control in blue and the composite treatment ST+SA+FA in purple. Data shows variations in each metric across treatments, with letters denoting statistical significance.</alt-text>
</graphic>
</fig>
<p>Application of SeNp significantly increased both fresh and dry weight of amaranth microgreen, which aligns with the findings of <xref ref-type="bibr" rid="B21">de los Santos-V&#xe1;zquez et al. (2016)</xref>, who reported that foliar application of Se at 5&#xa0;mg/L increased the biomass production and vitamin C content in lettuce by overwhelmed stress. Similarly, dry matter production and essential oil content were improved by applying SeNp under drought conditions in Basil (<xref ref-type="bibr" rid="B9">Asghari et al., 2023</xref>). The current study findings correlate with these findings and show that the combined application of biosynthesized SeNp (ST&#x2b;SA&#x2b;FA) can enhance drought tolerance and biomass production in amaranth microgreens under drought conditions and highlight the potential of SeNp as a sustainable tool for enhancing crop resilience and productivity in stress environments.</p>
</sec>
<sec id="s3-6">
<title>3.6 Effect of SeNP on amaranth biochemical parameters of amaranthus microgreens</title>
<p>The biochemical parameters of amaranth microgreens (Amaranthus var. Arka Suguna) viz., chlorophyll content, carotenoids, total phenols, flavonoids, antioxidants, carbohydrates, vitamin c, soluble proteins, total soluble sugars (TSS), enzymatic activity and Se accumulation, was influenced by biogenic synthesized SeNp. The results obtained in the study revealed that SeNp significantly enhances these biochemical parameters, promoting plant growth and stress tolerance under drought conditions. The photosynthetic efficiency of the crop plants was determined by the accumulation of chlorophyll content in the plant systems. In our study, chlorophyll content in the amaranth microgreen was significantly influenced by the combined application of SeNp (ST&#x2b;SA&#x2b;FA), recording the highest chlorophyll A and B (1.03 and 0.24&#xa0;mg/100&#xa0;g) content, along with higher carotenoid level (79.7&#xa0;mg/g) followed by ST&#x2b;SA (<xref ref-type="table" rid="T1">Table 1</xref>; <xref ref-type="fig" rid="F7">Figures 7A&#x2013;C</xref>). All other methods of application of SeNp show statistically similar results at the 5 percent significance level. These results were supported by the previous studies conducted by <xref ref-type="bibr" rid="B2">Abbas (2012)</xref>, who reported that Se influences Chlorophyll and carotenoid levels by controlling the redox status of leaves. Also, <xref ref-type="bibr" rid="B58">Vijayarengan (2013)</xref> and <xref ref-type="bibr" rid="B45">Marisamy et al. (2015)</xref> identified that Se application has protective effects on chloroplast enzymes and improves photosynthetic pigments. Additionally, applying selenium at 10 and 5&#xa0;&#xb5;M enhanced the photosynthetic pigments in cucumber leaves exposed to salt stress (<xref ref-type="bibr" rid="B31">Hawrylak-Nowak, 2009</xref>). The result suggested that applying biosynthesized SeNPs increases photosynthetic pigments of amaranth microgreens.</p>
<fig id="F7" position="float">
<label>FIGURE 7</label>
<caption>
<p>Effects of SeNPs and drought stress on <bold>(A)</bold> Chlorophyll A, <bold>(B)</bold> Chlorophyll B, <bold>(C)</bold> Carotenoid, <bold>(D)</bold> Total soluble salts, <bold>(E)</bold> Glucose, <bold>(F)</bold> Total Proteins, <bold>(G)</bold> Carbohydrates in Amaranth microgreens var. Arka Suguna. All the plants were drought-stressed with PEG (37.5&#xa0;mM). Control- No Nanoparticles applied, ST: Seed treatment with SeNPs (100&#xa0;ppm), ST &#x2b; SA: Seed treatment with SeNPs (100&#xa0;ppm) and Soil application with SeNPs (100&#xa0;ppm), ST &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm), ST &#x2b; SA &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm), Soil application with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm). Different letters demonstrate significant differences among the treatments (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g007.tif">
<alt-text content-type="machine-generated">Bar graphs labeled A to G show the effects of different treatments on various plant metrics: chlorophyll A, chlorophyll B, carotenoids, total soluble solids, glucose, total protein, and carbohydrates. Treatments are Control, ST, ST+SA, ST+FA, and ST+SA+FA. ST+SA+FA generally results in the highest values across all metrics. Error bars indicate variability, and different letters denote significant differences.</alt-text>
</graphic>
</fig>
<p>Combined application of SeNp (ST&#x2b;SA&#x2b;FA) recorded the highest phenolic content (6.23&#xa0;mg/g), while ST&#x2b;SA&#x2b;FA also showed increased flavonoid levels (11.4&#xa0;mg/g). The total antioxidant availability was highest in ST&#x2b;SA (23.6&#xa0;mg/g), followed by the combination of ST&#x2b;SA&#x2b;FA of SeNp (22.3&#xa0;mg/g) under drought conditions (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F8">Figures 8A&#x2013;C</xref>). These results are closely related to the findings of <xref ref-type="bibr" rid="B19">Chu et al. (2009)</xref>, who observed that Se application reduces ROS and malondialdehyde content while increasing phenolic and flavonoid levels in wheat under cold stress. Similarly, antioxidant activity and robust antioxidant potential of SeNps under both saline and non-saline conditions were reported by <xref ref-type="bibr" rid="B56">Shahraki et al. (2022)</xref> and <xref ref-type="bibr" rid="B30">Guleria et al. (2020)</xref>, implying their role in mitigating oxidative stress and enhancing plant growth and development. Earlier studies demonstrated that selenium nanoparticles (SeNPs) synthesized via green methods possess significant antioxidant activity (<xref ref-type="bibr" rid="B39">Kondaparrthi et al., 2019</xref>; <xref ref-type="bibr" rid="B48">Mellinas et al., 2019</xref>; <xref ref-type="bibr" rid="B15">Boroumand et al., 2019</xref>; <xref ref-type="bibr" rid="B23">Dumore and Mukhopadhyay, 2020</xref>). These findings align with the observed enhancement in total phenols, flavonoids, and antioxidant levels in Amaranthus microgreens following treatment with biosynthesized SeNPs (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F8">Figures 8A&#x2013;C</xref>).</p>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>Effect of SeNPs on biochemical parameters of Amaranth microgreens var. Arka Suguna in <italic>In-vivo</italic>.</p>
</caption>
<table>
<thead valign="top">
<tr style="background-color:#D9D9D9">
<th align="left">Treatments</th>
<th align="left">Total phenols (mg/g)</th>
<th align="left">Total flavonoids (mg/g)</th>
<th align="left">Total carbohydrate (mg/100&#xa0;g)</th>
<th align="left">Total soluble protein (mg/100&#xa0;g)</th>
<th align="left">Total antioxidant (mg/g)</th>
<th align="left">Vitamin-c (g/100&#xa0;g)</th>
<th align="left">Selenium content</th>
<th align="left">CAT activity (U/mg/min)</th>
<th align="left">SOD activity (U/mg/min)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Control</td>
<td align="left">4.44 &#xb1; 0.30<sup>c</sup>
</td>
<td align="left">4.31 &#xb1; 0.18<sup>d</sup>
</td>
<td align="left">301 &#xb1; 12.2<sup>e</sup>
</td>
<td align="left">65.3 &#xb1; 6.11<sup>e</sup>
</td>
<td align="left">16.2 &#xb1; 0.25<sup>d</sup>
</td>
<td align="left">15.6 &#xb1; 1.93<sup>d</sup>
</td>
<td align="left">0.60 &#xb1; 0.10<sup>d</sup>
</td>
<td align="left">10.65 &#xb1; 0.16<sup>d</sup>
</td>
<td align="left">0.032 &#xb1; 0.005<sup>d</sup>
</td>
</tr>
<tr>
<td align="left">ST</td>
<td align="left">4.68 &#xb1; 0.13<sup>c</sup>
</td>
<td align="left">4.68 &#xb1; 0.32<sup>d</sup>
</td>
<td align="left">387 &#xb1; 12.9<sup>d</sup>
</td>
<td align="left">109.3 &#xb1; 16.7<sup>d</sup>
</td>
<td align="left">19.8 &#xb1; 0.26<sup>c</sup>
</td>
<td align="left">21.1 &#xb1; 1.92<sup>c</sup>
</td>
<td align="left">4.54 &#xb1; 0.01<sup>c</sup>
</td>
<td align="left">11.32 &#xb1; 0.12<sup>c</sup>
</td>
<td align="left">0.044 &#xb1; 0.002<sup>c</sup>
</td>
</tr>
<tr>
<td align="left">ST&#x2b;SA</td>
<td align="left">5.94 &#xb1; 0.34<sup>ab</sup>
</td>
<td align="left">6.74 &#xb1; 0.20<sup>c</sup>
</td>
<td align="left">782 &#xb1; 8.72<sup>b</sup>
</td>
<td align="left">190.4 &#xb1; 21.5<sup>b</sup>
</td>
<td align="left">23.6 &#xb1; 0.15<sup>a</sup>
</td>
<td align="left">32.7 &#xb1; 0.35<sup>b</sup>
</td>
<td align="left">8.16 &#xb1; 0.23<sup>b</sup>
</td>
<td align="left">12.77 &#xb1; 0.14<sup>b</sup>
</td>
<td align="left">0.056 &#xb1; 0.002<sup>b</sup>
</td>
</tr>
<tr>
<td align="left">ST&#x2b;FA</td>
<td align="left">5.41 &#xb1; 0.53<sup>b</sup>
</td>
<td align="left">7.50 &#xb1; 0.05<sup>b</sup>
</td>
<td align="left">710 &#xb1; 25.1<sup>c</sup>
</td>
<td align="left">145.2 &#xb1; 8.38<sup>c</sup>
</td>
<td align="left">20.1 &#xb1; 0.86<sup>c</sup>
</td>
<td align="left">22.2 &#xb1; 1.92<sup>c</sup>
</td>
<td align="left">4.66 &#xb1; 0.02<sup>c</sup>
</td>
<td align="left">11.42 &#xb1; 0.10<sup>c</sup>
</td>
<td align="left">0.046 &#xb1; 0.001<sup>c</sup>
</td>
</tr>
<tr>
<td align="left">ST&#x2b;SA&#x2b;FA</td>
<td align="left">6.23 &#xb1; 0.11<sup>a</sup>
</td>
<td align="left">11.4 &#xb1; 0.40<sup>a</sup>
</td>
<td align="left">951 &#xb1; 45.0<sup>a</sup>
</td>
<td align="left">377.2 &#xb1; 10.5<sup>a</sup>
</td>
<td align="left">22.3 &#xb1; 0.35<sup>b</sup>
</td>
<td align="left">36.7 &#xb1; 3.34<sup>a</sup>
</td>
<td align="left">10.69 &#xb1; 0.04<sup>a</sup>
</td>
<td align="left">13.50 &#xb1; 0.11<sup>a</sup>
</td>
<td align="left">0.065 &#xb1; 0.002<sup>a</sup>
</td>
</tr>
<tr>
<td align="left">CD (p &#x2264; 0.05)</td>
<td align="left">0.59</td>
<td align="left">0.47</td>
<td align="left">44.88</td>
<td align="left">25.15</td>
<td align="left">0.82</td>
<td align="left">3.84</td>
<td align="left">0.20</td>
<td align="left">0.24</td>
<td align="left">0.003</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Control- No Nanoparticles applied, ST: Seed treatment with SeNPs (100&#xa0;ppm), ST &#x2b; SA: Seed treatment with SeNPs (100&#xa0;ppm) and Soil application with SeNPs (100&#xa0;ppm), ST &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm), ST &#x2b; SA &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm), Soil application with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm). Data presented in the table represents the mean &#xb1; SD (n &#x3d; 3) at the significance level of p &#x2264; 0.05.</p>
</fn>
<fn>
<p>
<sup>a-d</sup>represents the statistical significance among the treatments. Treatments with same letters are statically on-par with each other.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<fig id="F8" position="float">
<label>FIGURE 8</label>
<caption>
<p>Effects of SeNPs and drought stress on <bold>(A)</bold> Total Phenol, <bold>(B)</bold> Total flavonoid, <bold>(C)</bold> Total Antioxidant, <bold>(D)</bold> Vit C in Amaranth microgreens var. Arka Suguna. All the plants were drought-stressed with PEG (37.5&#xa0;mM). Control- No Nanoparticles applied, ST: Seed treatment with SeNPs (100&#xa0;ppm), ST &#x2b; SA: Seed treatment with SeNPs (100&#xa0;ppm) and Soil application with SeNPs (100&#xa0;ppm), ST &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm), ST &#x2b; SA &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm), Soil application with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm). Different letters demonstrate significant differences among the treatments (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g008.tif">
<alt-text content-type="machine-generated">Bar graphs comparing control, ST, ST+SA, ST+FA, and ST+SA+FA treatments in four categories: total phenols, total flavonoids, total antioxidants, and vitamin C content. Each graph shows different heights for each treatment, indicating varying concentrations. Labels 'a', 'b', 'c', and 'd' denote statistical significance. Color legend included.</alt-text>
</graphic>
</fig>
<p>Carbohydrate content was significantly higher in amaranth microgreens treated with ST&#x2b;SA&#x2b;FA of SeNp, recording a maximum of 951&#xa0;mg/100&#xa0;g, followed by ST&#x2b;SA of SeNp-treated microgreens (782&#xa0;mg/100&#xa0;g) under drought conditions (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F7">Figure 7G</xref>). Consistent with the reports of <xref ref-type="bibr" rid="B5">Alam et al. (2022)</xref> and <xref ref-type="bibr" rid="B63">Zhou et al. (2022)</xref>, selenium nanoparticles were shown to boost growth performance in stressed plants through enhanced carbohydrate metabolism. Likewise, vitamin C content is also higher in amaranth microgreen treated with ST&#x2b;SA&#x2b;FA of SeNp (36.7&#xa0;g/100&#xa0;g) under drought conditions (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F8">Figure 8D</xref>), in line with the findings of <xref ref-type="bibr" rid="B21">de los Santos-V&#xe1;zquez et al. (2016)</xref>, reported that application of SeNp improves antioxidant and vitamin C content in tomatoes and melons. These results suggest that SeNp enhances nutrient accumulation and drought tolerance in amaranth microgreens.</p>
<p>SeNPs and selenite significantly enhance total selenium accumulation and soluble protein content in crops such as soybean sprouts and potato tubers. However, the effects vary by species, in soybeans (<xref ref-type="bibr" rid="B55">Sarwar et al., 2020</xref>) leads to an increase in the accumulation of soluble proteins, whereas in soybean sprouts, soluble proteins get reduced (<xref ref-type="bibr" rid="B52">Rao et al., 2022</xref>). In this study, biosynthesized SeNPs elevated total soluble proteins in Amaranthus microgreens, with the highest levels in ST&#x2b;SA&#x2b;FA (377.2&#xa0;mg/100&#xa0;g) and the lowest in the control (65&#xa0;mg/100&#xa0;g) (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F7">Figure 7F</xref>). Glucose content was highest in ST&#x2b;FA (1.13% w/w), comparable to ST (1.10% w/w), while ST&#x2b;SA&#x2b;FA and ST&#x2b;SA showed slightly lower values (1.03% w/w) (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F7">Figure 7E</xref>). Total soluble solids (TSS) peaked in ST&#x2b;SA&#x2b;FA and ST&#x2b;SA (1.33% Brix), followed by ST and ST&#x2b;FA (1.20% Brix), with the control exhibiting the lowest (0.76% Brix) (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F7">Figure 7D</xref>). These findings align with reports that SeNPs improve sugar accumulation by enhancing stress resilience and metabolic activity, as seen in tomatoes treated with 10&#xa0;mg/L SeNPs (<xref ref-type="bibr" rid="B32">Hern&#xe1;ndez-Hern&#xe1;ndez et al., 2019</xref>). The present study confirms that biosynthesized SeNPs boost total soluble sugars in Amaranthus microgreens (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F7">Figures 7D,E</xref>).</p>
</sec>
<sec id="s3-7">
<title>3.7 Effect of SeNP on enzymatic activity</title>
<p>Selenium is an essential component of antioxidant enzymes, critically involved in scavenging reactive oxygen and nitrogen species to mitigate oxidative cellular damage. In the current investigation, catalase (CAT) activity reached its maximum in the ST&#x2b;SA&#x2b;FA treatment (13.50&#xa0;U/mg/min), with ST&#x2b;SA (12.77&#xa0;U/mg/min) showing comparable results, whereas the control group displayed the lowest activity (10.65&#xa0;U/mg/min) (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F9">Figure 9A</xref>). A parallel trend was observed for superoxide dismutase (SOD), where ST&#x2b;SA&#x2b;FA exhibited the highest activity (0.065&#xa0;U/mg/min), significantly surpassing the control (0.032&#xa0;U/mg/min), with intermediate treatments showing no statistically distinct effects (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F9">Figure 9B</xref>). These results corroborate earlier studies highlighting selenium&#x2019;s capacity to upregulate antioxidant enzymes, enhancing plant resilience under stress. For instance, <xref ref-type="bibr" rid="B36">Jiang et al. (2017)</xref> documented elevated SOD activity in selenium-supplemented maize, and <xref ref-type="bibr" rid="B33">Hussein et al. (2019)</xref> reported analogous antioxidant enzyme modulation. Further evidence from <xref ref-type="bibr" rid="B60">Wu et al. (2016)</xref> and <xref ref-type="bibr" rid="B46">Marslin et al. (2017)</xref> underscores selenium&#x2019;s ability to augment proline accumulation, peroxidase, and glutathione peroxidase (GPX) activity, collectively attenuating oxidative stress and lipid peroxidation. The present findings validate that biosynthesized selenium nanoparticles (SeNPs) markedly enhance CAT and SOD activity in Amaranthus microgreens (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F9">Figure 9</xref>), solidifying selenium&#x2019;s pivotal role in fortifying antioxidant defense mechanisms in plants.</p>
<fig id="F9" position="float">
<label>FIGURE 9</label>
<caption>
<p>Effects of SeNPs and drought stress on <bold>(A)</bold> Catalase, <bold>(B)</bold> SOD in Amaranth microgreens var. Arka Suguna. All the plants were drought stressed with PEG (37.5&#xa0;mM). Control- No Nanoparticles applied, ST: Seed treatment with SeNPs (100&#xa0;ppm), ST &#x2b; SA: Seed treatment with SeNPs (100&#xa0;ppm) and Soil application with SeNPs (100&#xa0;ppm), ST &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm), ST &#x2b; SA &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm), Soil application with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm). Different letters demonstrate significant differences among the treatments (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g009.tif">
<alt-text content-type="machine-generated">Bar charts show enzyme activity levels for different treatments. Chart A displays catalase activity, highest in ST+SA+FA and lowest in Control. Chart B shows SOD activity, also peaking in ST+SA+FA and lowest in Control. Each bar is labeled a to d, indicating statistical differences.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s3-8">
<title>3.8 Estimation of selenium content in amaranth seedling</title>
<p>Selenium is primarily absorbed by plant roots through sulfur transporters and incorporated into organic compounds, with its accumulation in shoots influenced by soil selenium availability and organic matter content (<xref ref-type="bibr" rid="B67">Terry et al., 2000</xref>; <xref ref-type="bibr" rid="B8">Arscott and Goldman, 2012</xref>). Similar dose-dependent selenium accumulation patterns have been reported in wheat, alfalfa, sunflower (<xref ref-type="bibr" rid="B42">Lintschinger et al., 2000</xref>; <xref ref-type="bibr" rid="B44">Lyons et al., 2005</xref>), Brassica species (<xref ref-type="bibr" rid="B11">Banuelos et al., 1997</xref>), kale (<xref ref-type="bibr" rid="B40">Lefsrud et al., 2006</xref>), and onion (<xref ref-type="bibr" rid="B12">Barak and Goldmon, 1997</xref>). The selenium content in Amaranthus microgreens was highest in the ST&#x2b;SA&#x2b;FA treatment (10.69&#xa0;mg/g), followed by ST&#x2b;SA (8.16&#xa0;mg/g), while the control exhibited minimal accumulation (0.60&#xa0;mg/g) (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F10">Figure 10</xref>). These findings align with previous studies demonstrating that soil-applied SeNPs significantly enhance selenium uptake in plants, as observed in bok choy, where root concentrations exceeded shoot levels (<xref ref-type="bibr" rid="B51">Ramos et al., 2010</xref>).</p>
<fig id="F10" position="float">
<label>FIGURE 10</label>
<caption>
<p>Effects of SeNPs and drought stress on the Selenium content in Amaranth microgreens var. Arka Suguna. All the plants were drought stressed with PEG (37.5&#xa0;mM). Control- No Nanoparticles applied, ST: Seed treatment with SeNPs (100&#xa0;ppm), ST &#x2b; SA: Seed treatment with SeNPs (100&#xa0;ppm) and Soil application with SeNPs (100&#xa0;ppm), ST &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm), ST &#x2b; SA &#x2b; FA: Seed treatment with SeNPs (100&#xa0;ppm), Soil application with SeNPs (100&#xa0;ppm) and Foliar application with SeNPs (100&#xa0;ppm). Different letters demonstrate significant differences among the treatments (<italic>p</italic> &#x3c; 0.05).</p>
</caption>
<graphic xlink:href="fnano-07-1621024-g010.tif">
<alt-text content-type="machine-generated">Bar chart showing selenium content (mg/g) across different treatments. Control shows the lowest content, followed by ST, ST+FA. ST+SA is higher, while ST+SA+FA is the highest. Error bars and significance letters (a, b, c, d) are included.</alt-text>
</graphic>
</fig>
<p>The current study confirms that biosynthesized SeNPs effectively promote selenium biofortification in Amaranthus microgreens (<xref ref-type="table" rid="T2">Table 2</xref>; <xref ref-type="fig" rid="F10">Figure 10</xref>), highlighting their potential for enhancing nutritional quality in leafy vegetables.</p>
</sec>
</sec>
<sec sec-type="conclusion" id="s4">
<title>4 Conclusion</title>
<p>This study highlights the significant potential of biosynthesized selenium nanoparticles (SeNPs) in enhancing abiotic stress tolerance and improving growth parameters in Amaranthus microgreens (var. Arka Suguna). The most effective treatments are seed treatment, soil application, and foliar spray (ST&#x2b;SA&#x2b;FA) of 100&#xa0;ppm SeNPs, resulting in remarkable improvements across all measured parameters. The treatment achieved a 97.5% germination rate, increased plant height to 5.6&#xa0;cm, and boosted yield to 330&#xa0;mg. Nutritionally, it enhanced protein content to 377.20&#xa0;mg/100&#xa0;g, carbohydrates to 951&#xa0;mg/100&#xa0;g, flavonoids to 11.40&#xa0;mg/g, and vitamin C to 36.67&#xa0;mg/100&#xa0;g. The antioxidant capacity significantly improved with SOD activity reaching 0.07&#xa0;U/mg/min and CAT activity 13.49&#xa0;U/mg/min, indicating stronger stress defense mechanisms. Notably, selenium accumulation peaked at 10.68&#xa0;mg/g, demonstrating effective biofortification. Beyond plant growth, the SeNPs showed compatibility with beneficial soil microorganisms, suggesting broader ecosystem benefits. These comprehensive results position biosynthesized SeNPs as a multifaceted solution for modern agriculture, capable of simultaneously addressing productivity challenges posed by abiotic stresses while improving nutritional quality. The findings strongly support the adoption of SeNPs as sustainable nano-fertilizers, offering an innovative approach to enhance crop performance under stressful environmental conditions. In the future, nano selenium can be mass-produced commercially for agricultural applications. This research provides a practical and environmentally friendly method of enhancing microgreen production and drought resistance, which is particularly beneficial for small-scale and urban agriculture farmers. Improving nutrient content supports food security in areas with limited water availability. The results also complement international sustainability objectives, calling for lesser dependency on chemical inputs in agriculture.</p>
<p>Recent studies have shown that selenium nanoparticles can induce epigenetic modifications by altering stress-related gene expression, such as DNA methylation in plants like chicory and pepper. These changes may contribute to enhanced abiotic stress tolerance. While transgenerational inheritance has not yet been confirmed, the potential for epigenetic memory warrants investigation. Long-term studies are necessary to assess whether such traits are retained and if they provide adaptive advantages in offspring under abiotic stress. A potential limitation of this study is the use of short-term microgreen trials under controlled conditions, which may not fully reflect the field-level responses. Future work should evaluate SeNPs effects across developmental stages and at different environmental conditions.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="s5">
<title>Data availability statement</title>
<p>The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.</p>
</sec>
<sec sec-type="author-contributions" id="s6">
<title>Author contributions</title>
<p>AG: Writing &#x2013; original draft, Writing &#x2013; review and editing, Conceptualization, Investigation, Data curation, Formal Analysis, Validation. RS: Formal Analysis, Investigation, Software, Validation, Visualization, Writing &#x2013; review and editing. IA: Conceptualization, Formal Analysis, Methodology, Software, Validation, Writing &#x2013; review and editing. RK: Data curation, Software, Validation, Visualization, Writing &#x2013; review and editing. AR: Formal Analysis, Investigation, Software, Validation, Visualization, Writing &#x2013; review and editing. AA: Data curation, Formal Analysis, Methodology, Software, Validation, Writing &#x2013; review and editing. SS: Conceptualization, Data curation, Investigation, Project administration, Resources, Supervision, Validation, Visualization, Writing &#x2013; original draft, Writing &#x2013; review and editing.</p>
</sec>
<sec sec-type="funding-information" id="s7">
<title>Funding</title>
<p>The author(s) declare that no financial support was received for the research and/or publication of this article.</p>
</sec>
<ack>
<p>The authors acknowledge the Department of Physics, Central University of Tamil Nadu, Thiruvarur, for sharing their instrumentation facility to complete the work successfully.</p>
</ack>
<sec sec-type="COI-statement" id="s8">
<title>Conflict of interest</title>
<p>The authors declare that the research 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="s9">
<title>Generative AI statement</title>
<p>The author(s) declare that no Generative AI was used in the creation of this manuscript.</p>
</sec>
<sec sec-type="disclaimer" id="s10">
<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>
<sec sec-type="supplementary-material" id="s11">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fnano.2025.1621024/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fnano.2025.1621024/full&#x23;supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="Table1.docx" id="SM1" mimetype="application/docx" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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