<?xml version="1.0" encoding="UTF-8" standalone="no"?>
<!DOCTYPE article PUBLIC "-//NLM//DTD Journal Publishing DTD v2.3 20070202//EN" "journalpublishing.dtd">
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" article-type="research-article" dtd-version="2.3" xml:lang="EN">
<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Mar. Sci.</journal-id>
<journal-title>Frontiers in Marine Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Mar. Sci.</abbrev-journal-title>
<issn pub-type="epub">2296-7745</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fmars.2024.1352529</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Marine Science</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Transcriptome analysis reveals ABA involved in the detoxification mechanism of macroalga <italic>Gracilariopsis lemaneiformis</italic> to cadmium toxicity</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Chen</surname>
<given-names>Xiaojiao</given-names>
</name>
<uri xlink:href="https://loop.frontiersin.org/people/1564692"/>
<role content-type="https://credit.niso.org/contributor-roles/data-curation/"/>
<role content-type="https://credit.niso.org/contributor-roles/visualization/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Tang</surname>
<given-names>Yueyao</given-names>
</name>
<role content-type="https://credit.niso.org/contributor-roles/methodology/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Sun</surname>
<given-names>Xue</given-names>
</name>
<uri xlink:href="https://loop.frontiersin.org/people/1565228"/>
<role content-type="https://credit.niso.org/contributor-roles/supervision/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Zhang</surname>
<given-names>Hao</given-names>
</name>
<uri xlink:href="https://loop.frontiersin.org/people/2028713"/>
<role content-type="https://credit.niso.org/contributor-roles/software/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Xu</surname>
<given-names>Nianjun</given-names>
</name>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/858923"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
<role content-type="https://credit.niso.org/contributor-roles/supervision/"/>
</contrib>
</contrib-group>
<aff id="aff1">
<institution>Key Laboratory of Marine Biotechnology of Zhejiang Province, School of Marine Sciences, Ningbo University</institution>, <addr-line>Ningbo, Zhejiang</addr-line>, <country>China</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Satheesh Sathianeson, King Abdulaziz University, Saudi Arabia</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Wenjun Wang, Chinese Academy of Fishery Sciences (CAFS), China</p>
<p>Shaharior Hossen, Chonnam National University, Republic of Korea</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Nianjun Xu, <email xlink:href="mailto:xunianjun@nbu.edu.cn">xunianjun@nbu.edu.cn</email>
</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>09</day>
<month>02</month>
<year>2024</year>
</pub-date>
<pub-date pub-type="collection">
<year>2024</year>
</pub-date>
<volume>11</volume>
<elocation-id>1352529</elocation-id>
<history>
<date date-type="received">
<day>11</day>
<month>12</month>
<year>2023</year>
</date>
<date date-type="accepted">
<day>25</day>
<month>01</month>
<year>2024</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2024 Chen, Tang, Sun, Zhang and Xu</copyright-statement>
<copyright-year>2024</copyright-year>
<copyright-holder>Chen, Tang, Sun, Zhang and Xu</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>
<sec>
<title>Introduction</title>
<p>Cadmium (Cd) is a significant threat environmental pollutant in the marine ecological environment offshore. The macroalga, <italic>Gracilariopsis lemaneiformis</italic>, of significant economic value, is widely cultivated along China&#x2019;s coastline. Yet, little is known about the molecular mechanisms underlying Cd tolerance in macroalga.</p>
</sec>
<sec>
<title>Methods</title>
<p>Here, we examined the transcriptome of <italic>G. lemaneiformis</italic> exposed to Cd to identify the responses to Cd stress.</p>
</sec>
<sec>
<title>Results and discussion</title>
<p>Our findings revealed that Cd led to the retardation of growth rate in <italic>G. lemaneiformis</italic>, accompanied by a notable reduction in the content of photosynthetic pigments and a decrease in the expression of genes associated with the photosynthetic system and nitrogen metabolism. When exposed to Cd, there was a rapid increase in Cd levels through the upregulation of genes encoding GlZIP6 and GlIRT1. Additionally, the expression of Cd efflux transporters, GlZIP1 and GlABCG22, and the ABCC7 transporter for compartmentation to the vacuole, was induced to mitigate Cd toxicity. Cd also activated crucial genes involved in the ABA biosynthesis and enhanced ABA content, thereby inducing ABA signaling pathway. Furthermore, exogenous ABA reduced the growth inhibition of <italic>G. lemaneiformis</italic> under Cd stress. Redox homeostasis was adjusted to adapt to Cd toxicity, with thioredoxin, glutaredoxin cycle and ascorbate-glutathione cycle identified as playing significant in maintaining reactive oxygen species homeostasis. Moreover, transcription factors such as several MYBs, signal transmission factors G protein and heat shock proteins (sHSPs, HSP 40, HSP 90, HSP101) were involved in the detoxification of Cd. Collectively, this study provided a comprehensive understanding of the molecular mechanisms underpinning the of responses of macroalga <italic>G. lemaneiformis</italic> to Cd exposure.</p>
</sec>
</abstract>
<kwd-group>
<kwd>Cd stress</kwd>
<kwd>macroalga</kwd>
<kwd>ABA</kwd>
<kwd>RNA-Seq</kwd>
<kwd>
<italic>Gracilariopsis lemaneiformis</italic>
</kwd>
</kwd-group>
<contract-sponsor id="cn001">Natural Science Foundation of Zhejiang Province<named-content content-type="fundref-id">10.13039/501100004731</named-content>
</contract-sponsor>
<counts>
<fig-count count="5"/>
<table-count count="3"/>
<equation-count count="0"/>
<ref-count count="58"/>
<page-count count="12"/>
<word-count count="5506"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-in-acceptance</meta-name>
<meta-value>Marine Molecular Biology and Ecology</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>Cadmium (Cd), an inherently toxic heavy metal and non-essential element, engenders deleterious repercussions on plant development (<xref ref-type="bibr" rid="B15">Haider et&#xa0;al., 2021</xref>), as well as animal and human health (<xref ref-type="bibr" rid="B21">Kumar and Sharma, 2019</xref>). In recent years, there has been a marked increase in industrial discharges and marine aquaculture operations, leading to heightened concentrations of Cd, a persistent environmental contaminant. Numerous studies have indicated that Cd is the primary polluted metal with high hazard indices to aquatic ecosystem along China&#x2019;s coast (<xref ref-type="bibr" rid="B46">Yu et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B54">Zhang et&#xa0;al., 2022a</xref>). For example, elevated levels of Cd have been detected in the water environment and sediments in electronic waste recycling areas in South China (<xref ref-type="bibr" rid="B17">Houessionon et&#xa0;al., 2021</xref>). Additionally, sedimentary deposits in the East China Sea coastal area (<xref ref-type="bibr" rid="B54">Zhang et&#xa0;al., 2022a</xref>), South China Sea (<xref ref-type="bibr" rid="B45">Xiao et&#xa0;al., 2022</xref>), and Bohai Bay (<xref ref-type="bibr" rid="B46">Yu et&#xa0;al., 2022</xref>) have all been contaminated by Cd.</p>
<p>The red alga, <italic>Gracilariopsis lemaneiformis</italic> (<italic>G. lemaneiformis</italic>), is a prominent economic macroalga cultivated in China&#x2019;s coastal region. It serves as the primary source of agar and is also a cornerstone resource for pharmaceuticals (<xref ref-type="bibr" rid="B58">Zou et&#xa0;al., 2004</xref>). Additionally, it is widely used as an effective bait for various piscine species and abalones (<xref ref-type="bibr" rid="B56">Zhu et&#xa0;al., 2017</xref>). <italic>G. lemaneiformis</italic> has been found to absorb Cd and significantly reduce Cd concentration in sediment (<xref ref-type="bibr" rid="B43">Wang et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B24">Luo et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B25">Luo et&#xa0;al., 2021</xref>). The bioconcentration factors of Cd in <italic>G. lemaneiformis</italic> can reach to 1000 times (<xref ref-type="bibr" rid="B43">Wang et&#xa0;al., 2014</xref>). Consequently, <italic>G. lemaneiformis</italic> holds considerable potential for <italic>in-situ</italic> bioremediation of Cd in coastal areas. To date, research has primarily focused on the impact of Cd on the growth, absorption, and accumulation of Cd in <italic>G. lemaneiformis</italic>. Beyond the evident growth effects, recent studies on the Cd toxicity have highlighted complex cellular and molecular variations in higher plants and microalgae (<xref ref-type="bibr" rid="B30">Rahman et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B48">Zhang et&#xa0;al., 2023a</xref>). A majority of these studies have explored changes using OMICS strategies such as transcriptomics, metabolomics, ionomics, proteomics, and genomics when plants and microalgae are exposed to Cd stress (<xref ref-type="bibr" rid="B30">Rahman et&#xa0;al., 2022</xref>). Transcriptomic strategies are frequently employed to determine the significance of transcripts under environmental stressors in plant species (<xref ref-type="bibr" rid="B30">Rahman et&#xa0;al., 2022</xref>). The molecular study on the transcriptome regulatory profile was performed under Cd toxicities and results revealed the stress-responsive genes, key metabolic pathways under Cd stress, and crucial genes involved in these metabolic reactions (<xref ref-type="bibr" rid="B5">Chen et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B47">Yu et&#xa0;al., 2023</xref>). Furthermore, the transcriptome analysis uncovered the detoxification mechanism and genes involved in detoxification, such as hormones, transcription factors, antioxidant, heavy metal transporters, plant hormones and calcium signals to Cd toxicity (<xref ref-type="bibr" rid="B31">Ramegowda et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B5">Chen et&#xa0;al., 2021</xref>).</p>
<p>Previous research has demonstrated that Cd has negatively impacts the on growth and development of <italic>G. lemaneiformis</italic> by reducing pigment content (<xref ref-type="bibr" rid="B44">Xia et&#xa0;al., 2004</xref>). To gain a deeper understanding of the molecular regulatory networks and tolerance mechanisms in macroalgae to Cd, we examined these processes at the transcriptional level. The study aimed to investigate <italic>G. lemaneiformis&#x2019;s</italic> stress response to Cd and identify the key genes involved in the detoxification processes. In the current study, we screened for a Cd concentration that caused moderate stress, measured Cd accumulation at various time points, and conducted a comparative transcriptome to investigate the genes responsive to Cd.</p>
</sec>
<sec id="s2" sec-type="materials|methods">
<label>2</label>
<title>Materials and methods</title>
<sec id="s2_1">
<label>2.1</label>
<title>Culture conditions</title>
<p>In this study, <italic>G. lemaneiformis</italic> strain 981 was collected from Ningde aquaculture base (Fujian, China (26&#xb0;65&#x2032;N, 119&#xb0;66&#x2032;E). Upon arrival at the laboratory, the attached sediment and coexisting algae adhering to <italic>G. lemaneiformis</italic> were eliminated thorough washing with sterile seawater. Subsequently, the robust <italic>G. lemaneiformis</italic> were cultivated under controlled conditions in an incubator for a duration of one week. The rhizoids with similar branching and length (13 &#xb1; 1&#xa0;cm with the rhizome tip) were used for experiment and cultured at 23&#xb0;C with a photoperiod of 12&#xa0;h light: 12&#xa0;h darkness and a light intensity of 50 &#x3bc;mol photons m<sup>-2</sup>s<sup>-1</sup> light intensity.</p>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>Determination of relative growth rate, pigments, and glutathione content</title>
<p>The relative growth rate (RGR) was detected at 1, 2, 4 and 6&#xa0;d post-Cd treatment with utilizing concentration of 50, 100, and 200 &#xb5;M. The RGR was calculated using the formula established by <xref ref-type="bibr" rid="B57">Zou and Gao (2014)</xref>: RGR (%) = Ln (W<sub>t</sub>/W<sub>0</sub>) &#xd7;100. Here, Wt represents the fresh weight at the corresponding time point, while W0 represents the initial time point. Each treatment had three biological replicates.</p>
<p>The content of photosynthetic pigments and glutathione (GSH) content was determined at 6&#xa0;d after Cd treatment in <italic>G. lemaneiformis</italic>. Photosynthetic pigments, phycoerythrin (PE) and phycocyanin (PC), were extracted with 50 mM PBS (pH 6.8). The extraction solution was centrifuged, and the absorbance was measured at 455, 564, 592, 618, and 645 nm by a spectrophotometer according to <xref ref-type="bibr" rid="B33">Sampath-Wiley and Neefus (2007)</xref> and <xref ref-type="bibr" rid="B6">Chen et&#xa0;al. (2022a)</xref>. Chlorophyll a (Chl a) and carotenoids (Car) were extracted using methanol (5 mL) with 0.1&#xa0;g <italic>G. lemaneiformis</italic> overnight in dark at 4&#xb0;C. Then, the extracts were centrifuged at 10,000 rpm for 15&#xa0;min at 4&#xb0;C and measured at 480, 510, 652, 665, and 750 nm using full wavelength spectrophotometer according to the procedures described by <xref ref-type="bibr" rid="B20">Ji et&#xa0;al. (2019)</xref>. GSH content quantified using colorimetric assay kits from Comin Bio. (Suzhou, China). In detail, approximately 0.1&#xa0;g fresh sample extracted with 1 mL 50 mM PBS (pH 6.8) at 4&#xb0;C and centrifuged at 8,000 rpm for 10&#xa0;min at 4&#xb0;C. Then, the supernatant reacted with 5,5&#x2019;-dithiobis-2-nitrobenoicacid (DTNB) and measured at 412 nm by a spectrophotometer. Every physiological indicator each treatment had three biological replicates.</p>
</sec>
<sec id="s2_3">
<label>2.3</label>
<title>Determination of Cd content and bioconcentration factors</title>
<p>Cd level was quantified at 1, 3, 6, 12, 24&#xa0;h, 3&#xa0;d and 6&#xa0;d after 75 &#xb5;M of Cd treatment. Each time point had three biological replicates. In detail, the collected samples were rinsed thoroughly for 6 cycles with deionized water and dried in an oven at 80&#xb0;C for 24&#xa0;h. Then, the desiccated sample (0.1&#xa0;g) was ground for nitric acid digestion. The quantification of Cd content was executed via an inductively coupled plasma mass spectrometry (ICP-MS, iCAP RQ, Thermo Fisher Scientific, CA, USA) (<xref ref-type="bibr" rid="B55">Zhao et&#xa0;al., 2022</xref>).</p>
<p>The bioconcentration factor (BCF) is determined by the ratio q/c, which signifies degree of enrichment level of a specific chemical in living organisms (<xref ref-type="bibr" rid="B12">Foster, 1976</xref>). The term &#x201c;q (mg/kg DW)&#x201d; represents the concentration of Cd content found in <italic>G. lemaneiformis</italic>, while &#x201c;c (mg/L)&#x201d; signifies the dissolved Cd concentration within a solution.</p>
</sec>
<sec id="s2_4">
<label>2.4</label>
<title>ABA quantification</title>
<p>Abscisic acid (ABA) measurement was performed using high-performance liquid chromatography-electrospray ionization-tandem mass spectrometry (HPLC-ESI-MS/MS) according to <xref ref-type="bibr" rid="B36">Shao et&#xa0;al. (2019)</xref> with some modifications. <italic>G. lemaneiformis</italic> samples (1.0&#xa0;g fresh weight) were ground in liquid nitrogen and extracted at 4&#xb0;C overnight with methanol containing 0.2% formic acid (FA) that had been spiked with internal standards. The extracts were centrifuged 1,4000 rpm at 4&#xb0;C, and the resulting supernatants were dried under N<sub>2</sub>. The obtained pellet was then resuspended with 200 &#x3bc;L of 50% methanol (1:1, v/v), centrifuged before HPLC-ESI-MS/MS analysis. The mobile phases consisted of solvent A (0.04% [v/v] formic acid (FA) in water) and solvent B (0.04% [v/v] FA in acetonitrile). Samples were placed in an automatic sampler at 4&#xb0;C with an injection volume of 4 &#x3bc;L. The column temperature was maintained at 45&#xb0;C, and a flow rate of 400 &#x3bc;L/min was employed. The linear gradient was programmed as follows: 0-10&#xa0;min, transitioning from 2 to 98% solvent B (v/v), 10-11.1&#xa0;min, transitioning from 98 to 2% solvent B (v/v), and 11.1-13&#xa0;min, hold at 2% solvent B. A Qtrap 5500 System (AB Sciex) was used for mass spectrometry in negative ion mode and multiple reaction monitoring modes. Data was analyzed using Multiquant 3.03 software.</p>
</sec>
<sec id="s2_5">
<label>2.5</label>
<title>RNA sequencing and analysis of differentially expressed genes</title>
<p>Total RNA was extracted from <italic>G. lemaneiformis</italic> samples (0.1&#xa0;g fresh weight) using the RNeasy Plant Mini Kit (Qiagen, Hilden, Germany). Each treatment had three biological replicates. RNA-seq was performed by BGI (Shenzhen, China). SOAPnuke (<ext-link ext-link-type="uri" xlink:href="https://github.com/BGI-flexlab/SOAPnuke">https://github.com/BGI-flexlab/SOAPnuke</ext-link>) was used to remove reads containing adapter sequences or more than 10% unidentified nucleotides and low-quality reads to obtain clean read databases. The clean data were mapped to the reference transcripts, which combined the transcripts from genomic annotation and full-length transcripts obtained by SMRT-Seq (<xref ref-type="bibr" rid="B7">Chen et&#xa0;al., 2022b</xref>), by Bowtie2 (<ext-link ext-link-type="uri" xlink:href="https://bowtie-bio.sourceforge.net/bowtie2/index.shtml">https://bowtie-bio.sourceforge.net/bowtie2/index.shtml</ext-link>). Expectation Maximization (RSEM) tool was applied to calculate the transcript abundance of each gene in each sample based on fragments per kilobase per million reads (FPKM) (<xref ref-type="bibr" rid="B22">Li and Dewey, 2011</xref>).</p>
<p>The differentially expressed genes (DEGs) was identified based on the criterion of |log2 [fold-change (FC)]| &#x2265; 1 and an adjusted P value (Q value) &#x2264; 0.001. The Gene Ontology (GO) (<ext-link ext-link-type="uri" xlink:href="https://www.geneontology.org/">https://www.geneontology.org/</ext-link>) term and Kyoto Encyclopedia of Genes and Genomes (KEGG) (<ext-link ext-link-type="uri" xlink:href="https://www.genome.jp/kegg/">https://www.genome.jp/kegg/</ext-link>) pathway significantly enriched in DEGs were obtained by performing GO and KEGG enrichment analysis, respectively. A Q value &#x2264; 0.01 was used to determine if a GO term was significantly enriched, while a P value &#x2264; 0.05 was used to determine if a KEGG pathway was significantly enriched.</p>
<p>The Swiss-Prot (<ext-link ext-link-type="uri" xlink:href="http://web.expasy.org/compute_pi/">http://web.expasy.org/compute_pi/</ext-link>), Cell-PLoc 2.0 (<ext-link ext-link-type="uri" xlink:href="http://www.csbio.sjtu.edu.cn/bioinf/Cell-PLoc-2/">http://www.csbio.sjtu.edu.cn/bioinf/Cell-PLoc-2/</ext-link>), and InterPro (<ext-link ext-link-type="uri" xlink:href="http://prosite.expast.org/">http://prosite.expast.org/</ext-link>) databases were utilized to predict the molecular weight, subcellular localization, and domains of genes, respectively.</p>
</sec>
<sec id="s2_6">
<label>2.6</label>
<title>Quantitative real-time RT-PCR analysis</title>
<p>For the validation of transcriptome results, six DEGs were randomly selected for qRT-PCR analysis. The method of qRT-PCR was according to our previous study (<xref ref-type="bibr" rid="B6">Chen et&#xa0;al., 2022a</xref>). Gene-specific primer pairs are listed in <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S1</bold>
</xref>. As the internal reference gene, <italic>actin</italic> was employed, and the relative expression of the target gene was calculated by the 2<sup>-&#x394;&#x394;Ct</sup> method (<xref ref-type="bibr" rid="B23">Livak and Schmittgen, 2001</xref>).</p>
</sec>
<sec id="s2_7">
<label>2.7</label>
<title>Statistical analysis</title>
<p>The presentation of data was achieved as mean &#xb1; standard deviation (SD), with n = 3 replicates. The Univariate General Linear Models procedure of SPSS Statistics 22.0 was applied to analyze the statistical significance of the data. One-way ANOVA and Duncan&#x2019;s multiple range tests were used to separate treatment averages at P &lt;0.05 and P &lt;0.01.</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<label>3</label>
<title>Results and discussion</title>
<sec id="s3_1">
<label>3.1</label>
<title>Impact of Cd stress on growth and pigments content of <italic>G. lemaneiformis</italic>
</title>
<p>With the escalation of Cd concentration ranging from 50 to 500 &#x3bc;M, a substantial reduction in the RGR of <italic>G. lemaneiformis</italic> was observed (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figures&#xa0;1A, B</bold>
</xref>). The algal biomass exhibited complete discoloration and lethality at a Cd concentration of 500 &#x3bc;M (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure&#xa0;1A</bold>
</xref>). At 50 &#x3bc;M of Cd, the RGR exhibited a decline from 12.8% on the 1st day to 47.0% on the 6th day. Furthermore, the branching pattern of <italic>G. lemaneiformis</italic> displayed shorter and fewer branches compared to the control (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure&#xa0;1</bold>
</xref>). At a Cd concentration of 100 &#x3bc;M, the RGR registered a decrease of 63.5% on the 6th day, accompanied by the emergence of white branches. Notably, the growth was significantly suppressed at 200 &#x3bc;M Cd concentration, resulting in a 93.5% decline in RGR by the 6th day. This phenomenon was similar to previous studies by <xref ref-type="bibr" rid="B44">Xia et&#xa0;al. (2004)</xref>, the RGR in 50, 100, 200 &#x3bc;M Cd-treatments decreased by 7.0%, 46.3% and 89.4% for 96&#xa0;h.</p>
<p>Moreover, at the same Cd concentrations of 50-200 &#x3bc;M, the content of photosynthetic pigments, PE, PC and Chl <italic>a</italic>, exhibited marked diminishment by 24.6-38.4%, 32.3-53.4% and 6.5-13.7% after 6&#xa0;d of Cd treatment, respectively (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figures&#xa0;1C&#x2013;E</bold>
</xref>). In contrast, the content of GSH significantly increased in a dose-dependent manner within the range of 50&#x2013;200 &#x3bc;M Cd by 11.7&#x2013;37 folds (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure&#xa0;1F</bold>
</xref>). Glutathione, the heavy metal chelating agent, chelates with Cd already located inside cells for detoxification (<xref ref-type="bibr" rid="B11">Fang et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B9">Das et&#xa0;al., 2021</xref>). In many studies, Cd has proved to induce an increase in GSH content (<xref ref-type="bibr" rid="B14">Gao et&#xa0;al., 2022</xref>), in consistent with our result.</p>
<p>To avoid a severe growth inhibition of <italic>G. lemaneiformis</italic>, the IC<sub>50</sub> value corresponding to a 50% reduction in RGR was selected for further studies at 6&#xa0;d after stress. By virtue of linear interpolation, the determined IC<sub>50</sub> value of Cd was 75 &#x3bc;M.</p>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Cd accumulation in <italic>G. lemaneiformis</italic>
</title>
<p>In this section, we investigate the accumulation of Cd in <italic>G. lemaneiformis</italic>. The accumulation process is crucial to understanding the impact of environmental pollutants on aquatic ecosystems and the potential for bioaccumulation. To clarify the dynamics of Cd uptake in <italic>G. lemaneiformis</italic>, the accumulation of Cd in the algal was determined (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>). The Cd content increased rapidly within 12&#xa0;h and reached a maximum at day 3, suggesting that <italic>G. lemaneiformis</italic> can quickly absorb Cd. The BCF of <italic>G. lemaneiformis</italic> ranged from 4.86 to 28.46 during the experimental period. In particular, the accumulation of Cd accounted for 54% and 93% of its maximum capacity at 1 and 3&#xa0;d after Cd stress, respectively. <xref ref-type="bibr" rid="B43">Wang et&#xa0;al. (2014)</xref> reported that the maximum absorption of low concentration Cd (1, 5, 10, and 20 &#x3bc;g/L) in <italic>G. lemaneiformis</italic> was between 20-30 days and the BCF was 463- 1113. Our results revealed that <italic>G. lemaneiformis</italic> can quickly absorb Cd at high concentration for bioremediation.</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Content of Cd (mg/kg DW) accumulated in <italic>G. lemaneiformis</italic> under Cd treatment.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="left">Times after treatment</th>
<th valign="middle" align="left">Content of Cd (mg/kg)</th>
<th valign="middle" align="center">BCF</th>
<th valign="middle" align="left">Ratio<sup>#</sup>
</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="center">0</td>
<td valign="middle" align="center">0.45 &#xb1; 0.03</td>
<td valign="top" align="center"/>
<td valign="middle" align="left"/>
</tr>
<tr>
<td valign="middle" align="center">1 h</td>
<td valign="middle" align="center">40.84 &#xb1; 4.14</td>
<td valign="top" align="right">4.86</td>
<td valign="middle" align="right">17%</td>
</tr>
<tr>
<td valign="middle" align="center">6 h</td>
<td valign="middle" align="center">70.92 &#xb1; 2.74</td>
<td valign="top" align="right">8.44</td>
<td valign="middle" align="right">30%</td>
</tr>
<tr>
<td valign="middle" align="center">12 h</td>
<td valign="middle" align="center">101.35 &#xb1; 5.16</td>
<td valign="top" align="right">12.07</td>
<td valign="middle" align="right">42%</td>
</tr>
<tr>
<td valign="middle" align="center">1 d</td>
<td valign="middle" align="center">129.17 &#xb1; 10.55</td>
<td valign="top" align="right">15.38</td>
<td valign="middle" align="right">54%</td>
</tr>
<tr>
<td valign="middle" align="center">3 d</td>
<td valign="middle" align="center">221.52 &#xb1; 26.13</td>
<td valign="top" align="right">26.37</td>
<td valign="middle" align="right">93%</td>
</tr>
<tr>
<td valign="middle" align="center">6 d</td>
<td valign="middle" align="center">239.03 &#xb1; 20.10</td>
<td valign="top" align="right">28.46</td>
<td valign="middle" align="right">100%</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>
<sup>#</sup> Indicates the ratio of Cd content at the corresponding time to that at 6&#xa0;d.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s3_3">
<label>3.3</label>
<title>Transcriptome analysis and gene functional annotation</title>
<p>To clarify the responsive gene to Cd, we performed transcriptomes analysis of <italic>G. lemaneiformis</italic> at 1 and 3&#xa0;d after Cd stress. After removing adaptors, N&gt;10 and low-quality reads, the clean reads were aligned to reference transcripts with an overall mapping rate of 91-92%. In a result, 22,806 transcripts were expressed. Among these, 13,800, 12,088, 18,856, 320 and 125 transcripts were annotated to GO, KEGG, RefSeq non-redundant proteins (NR), Transcription factors (TFs) and Plant Resistance Gene (PRG) public databases, respectively. Approximately 82.9% of these transcripts were annotated in at least one database.</p>
</sec>
<sec id="s3_4">
<label>3.4</label>
<title>Identification and validation of differentially expressed genes</title>
<p>For comparison, 1967 (998 up and 969 down) and 3369 (1850 up and 1519 down) DEGs were identified at 1 and 3&#xa0;d after Cd stress, respectively (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figures&#xa0;2A, B</bold>
</xref>). This result showed that the gene response was enhanced in <italic>G. lemaneiformis</italic> with the increase of Cd accumulation. Moreover, 1192 (592 up and 474 down) of the DEGs were co-regulated at 1 and 3&#xa0;d after treatment (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure&#xa0;2C</bold>
</xref>). The qRT-PCR results were consistent with those of RNA-Seq (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S1</bold>
</xref>), which verified the reliability of RNA-Seq.</p>
</sec>
<sec id="s3_5">
<label>3.5</label>
<title>GO, KEGG enrichment of DEGs</title>
<p>GO enrichment analysis of DEGs revealed that numerous GO terms were influenced by Cd. The molecular function, including &#x201c;pigment binding&#x201d;, &#x201c;antioxidant activity&#x201d;, &#x201c;transmembrane transporter activity&#x201d;, biological regulation such as &#x201c;response to far red light&#x201d; and &#x201c;photosynthesis&#x201d;, &#x201c;ROS biosynthetic process&#x201d;, &#x201c;cellular oxidant detoxification&#x201d; were observed at 1 and 3&#xa0;d in response to Cd stress. Furthermore, cellular component including &#x201c;plastoglobule&#x201d;, &#x201c;plastid thylakoid membrane&#x201d; and &#x201c;photosynthetic membrane&#x201d; were also implicated (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>). The GO terms &#x201c;detoxification&#x201d;, &#x201c;antioxidant activity&#x201d;, and &#x201c;signal transducer activity&#x201d;, which may play key roles in abiotic stress and &#x201c;membrane&#x201d; were also found in kenaf in the response to Cd exposure (<xref ref-type="bibr" rid="B5">Chen et&#xa0;al., 2021</xref>).</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>The top20 of GO enrichment terms of DEGs after Cd treatment at 1&#xa0;d <bold>(A)</bold>, 3d <bold>(B)</bold> and co-expressed at 1 and 3&#xa0;d <bold>(C)</bold>.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-11-1352529-g001.tif"/>
</fig>
<p>KEGG pathway analysis revealed that DEGs at 1 and 3&#xa0;d were predominantly associated with metabolism processes, including energy metabolism and carbohydrate metabolism, as well as cellular processes such as &#x201c;peroxisome&#x201d; and &#x201c;transporter&#x201d; and &#x201c;MAPK signaling pathway&#x2013;plant&#x201d; (<xref ref-type="table" rid="T2">
<bold>Table&#xa0;2</bold>
</xref>). These data suggested that genes related to photosynthesis system, antioxidant activity, transmembrane transporter activity, energy metabolism, carbohydrate metabolism, and MAPK signaling pathway &#x2013; plant play a crucial role in the response to Cd exposure in <italic>G. lemaneiformis</italic>.</p>
<table-wrap id="T2" position="float">
<label>Table&#xa0;2</label>
<caption>
<p>The KEGG pathway of DEGs after Cd treatment at 1&#xa0;d, 3d and co-expressed at 1 and 3&#xa0;d.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="left">Level 1</th>
<th valign="middle" align="left">Level 2</th>
<th valign="middle" align="left">Pathway Name</th>
<th valign="middle" align="left">p-value</th>
</tr>
</thead>
<tbody>
<tr>
<th valign="middle" colspan="4" align="left">1d DEGs</th>
</tr>
<tr>
<td valign="middle" rowspan="6" align="left">Metabolism</td>
<td valign="middle" rowspan="2" align="left">Energy metabolism</td>
<td valign="middle" align="left">Photosynthesis - antenna proteins</td>
<td valign="middle" align="right">0</td>
</tr>
<tr>
<td valign="middle" align="left">Nitrogen metabolism</td>
<td valign="middle" align="right">1.61E-08</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="left">Amino acid metabolism</td>
<td valign="middle" align="left">Arginine and proline metabolism</td>
<td valign="middle" align="right">0.001620093</td>
</tr>
<tr>
<td valign="middle" align="left">Tryptophan metabolism</td>
<td valign="middle" align="right">0.039183466</td>
</tr>
<tr>
<td valign="middle" align="left">Metabolism of cofactors and vitamins</td>
<td valign="middle" align="left">Porphyrin and chlorophyll metabolism</td>
<td valign="middle" align="right">0.010109623</td>
</tr>
<tr>
<td valign="middle" align="left">Carbohydrate metabolism</td>
<td valign="middle" align="left">Ascorbate and aldarate metabolism</td>
<td valign="middle" align="right">0.022687861</td>
</tr>
<tr>
<td valign="middle" align="left">Cellular Processes</td>
<td valign="middle" align="left">Transport and catabolism</td>
<td valign="middle" align="left">Peroxisome</td>
<td valign="middle" align="right">2.22E-04</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="left">Environmental Information Processing</td>
<td valign="middle" align="left">Membrane transport</td>
<td valign="middle" align="left">ABC transporters</td>
<td valign="middle" align="right">2.57E-04</td>
</tr>
<tr>
<td valign="middle" align="left">Signal transduction</td>
<td valign="middle" align="left">MAPK signaling pathway - plant</td>
<td valign="middle" align="right">0.007485428</td>
</tr>
<tr>
<th valign="middle" colspan="4" align="left">3d DEGs</th>
</tr>
<tr>
<td valign="middle" rowspan="4" align="left">Metabolism</td>
<td valign="middle" rowspan="2" align="left">Energy metabolism</td>
<td valign="middle" align="left">Photosynthesis - antenna proteins</td>
<td valign="middle" align="right">6.36E-12</td>
</tr>
<tr>
<td valign="middle" align="left">Nitrogen metabolism</td>
<td valign="middle" align="right">1.70E-07</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="left">Carbohydrate metabolism</td>
<td valign="middle" align="left">Amino sugar and nucleotide sugar metabolism</td>
<td valign="middle" align="right">0.011918623</td>
</tr>
<tr>
<td valign="middle" align="left">Glyoxylate and dicarboxylate metabolism</td>
<td valign="middle" align="right">0.012830692</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="left">Cellular Processes</td>
<td valign="middle" rowspan="2" align="left">Transport and catabolism</td>
<td valign="middle" align="left">Peroxisome</td>
<td valign="middle" align="right">4.97E-04</td>
</tr>
<tr>
<td valign="middle" align="left">Phagosome</td>
<td valign="middle" align="right">7.73E-04</td>
</tr>
<tr>
<td valign="middle" align="left">Environmental Information Processing</td>
<td valign="middle" align="left">Signal transduction</td>
<td valign="middle" align="left">MAPK signaling pathway - plant</td>
<td valign="middle" align="right">0.004885049</td>
</tr>
<tr>
<th valign="middle" colspan="4" align="left">1d and 3d co-regulated</th>
</tr>
<tr>
<td valign="middle" rowspan="3" align="left">Metabolism</td>
<td valign="middle" rowspan="2" align="left">Energy metabolism</td>
<td valign="middle" align="left">Photosynthesis - antenna proteins</td>
<td valign="middle" align="right">3.33E-16</td>
</tr>
<tr>
<td valign="middle" align="left">Nitrogen metabolism</td>
<td valign="middle" align="right">9.29E-09</td>
</tr>
<tr>
<td valign="middle" align="left">Metabolism of cofactors and vitamins</td>
<td valign="middle" align="left">Porphyrin and chlorophyll metabolism</td>
<td valign="middle" align="right">0.001713765</td>
</tr>
<tr>
<td valign="middle" align="left">Cellular Processes</td>
<td valign="middle" align="left">Transport and catabolism</td>
<td valign="middle" align="left">Peroxisome</td>
<td valign="middle" align="right">1.16E-04</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3_6">
<label>3.6</label>
<title>Specific differentially expressed genes in response to Cd</title>
<sec id="s3_6_1">
<label>3.6.1</label>
<title>DEGs involved in signal transduction and ABA biosynthesis pathway</title>
<p>In MAPK signal-plant pathway, we found that many pathways generated by signaling molecules and stress-induced were affected by Cd stress. However, most of genes involved in these pathways were down-regulated by Cd, for example, FLS2 involved in fg22-mediated disease resistance, NDPK2 mediated by H<sub>2</sub>O<sub>2</sub>, CAM4 mediated by wounding (<xref ref-type="fig" rid="f2">
<bold>Figures&#xa0;2A, B</bold>
</xref>). Whereas, Cd activated genes encoding serine/threonine-protein kinase SRK2 (SnRK2) involved in ABA signaling pathway (<xref ref-type="fig" rid="f2">
<bold>Figures&#xa0;2A, B</bold>
</xref>). Moreover, the expression of downstream genes encoding ABA responsive element binding factor (ABF) and MKK3 was enhanced by 1.1-1.4 folds and 1.2-1.5 folds, respectively by Cd (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S3</bold>
</xref>). Furthermore, expression of key genes encoding 15-cis-phytoene desaturase (PDS), prolycopene isomerase (crtISO) and zeaxanthin epoxidase (ZEP) involved in ABA biosynthesis pathway was also induced by Cd (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2C</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S3</bold>
</xref>).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>The expression profiles of Cd-responsive genes involved in MAPK signaling pathway-plant <bold>(A, B)</bold>, ABA pathway <bold>(C)</bold> and the effect of Cd on ABA content <bold>(D)</bold>, and the effect of ABA on the RGR <bold>(E)</bold>, PE <bold>(F)</bold>, PC <bold>(G)</bold> in <italic>G. lemaneiformis</italic> under Cd stress. Each circle beside the name of genes represents the abundance change of corresponding DEGs at 1&#xa0;d (left) and 3&#xa0;d (right), respectively. The red arrows next to the metabolite represent a significant increase in the content of metabolite. The different letters on the 2 columns indicate significant differences between different concentrations of treatments (P &lt; 0.05).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-11-1352529-g002.tif"/>
</fig>
<p>As the enhanced expression of genes related to the ABA synthesis pathway was observed in <italic>G. lemaneiformis</italic> after Cd stress, ABA content quantified 1 day post-stress using UPLC-MS. The MS data and retention times of ABA are detailed in <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S2</bold>
</xref>. Notably, the presence of Cd led to a 34.5% remarkable increase in ABA content (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2D</bold>
</xref>).</p>
<p>Considering the content of hormones and expression profiles, we conducted that ABA might be play a positive role in response to Cd stress in <italic>G. lemaneiformis.</italic> To further verify the effect of ABA on growth of <italic>G. lemaneiformis</italic> under Cd stress, different concentrations of ABA were applied to <italic>G. lemaneiformis</italic> under 75 &#xb5;M Cd stress. At 10 &#xb5;M, ABA reduced the inhibition of Cd on the growth of <italic>G. lemaneiformis</italic> and increased the contents of PE and PC (<xref ref-type="fig" rid="f2">
<bold>Figures&#xa0;2E&#x2013;G</bold>
</xref>). A number of reports have demonstrated that ABA is closely related to perception and mediation of Cd stress (<xref ref-type="bibr" rid="B32">Rasafi et&#xa0;al., 2020</xref>). For instance, in rice seedlings and lettuce, there is a rapid enhancement of ABA content under Cd stress (<xref ref-type="bibr" rid="B18">Hsu and Kao, 2003</xref>; <xref ref-type="bibr" rid="B38">Tang et&#xa0;al., 2020</xref>), and in <italic>Arabidopsis thaliana</italic> exogenous application of ABA has been shown to significantly decreased Cd content and alleviated Cd toxicity (<xref ref-type="bibr" rid="B26">Meng et&#xa0;al., 2022</xref>). <xref ref-type="bibr" rid="B41">Wang et&#xa0;al. (2022)</xref> reported that gene involved in ABA signaling pathway can enhance Cd resistance ability of <italic>T. hispida</italic> by regulating the production of ROS under Cd stress. Our results revealed that ABA and ABA signal may be involved in the induction of protective mechanisms against Cd toxicity in G. <italic>lemaneiformis</italic>.</p>
</sec>
<sec id="s3_6_2">
<label>3.6.2</label>
<title>DEGs involved in antioxidant system</title>
<p>GO enrichment analysis revealed that &#x201c;antioxidant activity&#x201d; and &#x201c;cellular oxidant detoxification&#x201d; was involved in the response to Cd. The antioxidant system may play key roles in Cd stress in plants (<xref ref-type="bibr" rid="B49">Zhang and Reynolds, 2019</xref>). In plants, the antioxidant defense system mainly consists of superoxide mutase (SOD), which converts oxygen radicals (O<sup>2&#x2212;</sup>) into hydrogen peroxide (H<sub>2</sub>O<sub>2</sub>), and L-ascorbate peroxidase (APX), peroxidase (POD), and catalase (CAT), these three enzymes remove toxic H<sub>2</sub>O<sub>2</sub> (<xref ref-type="bibr" rid="B49">Zhang and Reynolds, 2019</xref>). Furthermore, the sulfur-containing antioxidant including thioredoxin (Trx), ascorbate (AsA) -GSH cycle and glutaredoxin cycle, etc., may also involve in the detoxification of Cd (<xref ref-type="bibr" rid="B37">Smiri et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B51">Zhang et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B48">Zhang et&#xa0;al., 2023a</xref>). A total of 6 (3 upregulated and 3 downregulated) and 12 (8&#xa0;upregulated and 4 downregulated) DEGs associated with antioxidant activity were identified at 1 and 3d after Cd stress, respectively (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>). Among them, expression of 2 SOD encoding genes (<italic>SOD3</italic> and <italic>EC-SOD</italic>) and 2 of 3 CAT encoding genes (<italic>CAT-B</italic>, <italic>CAT</italic>) was down-regulated, while APX encoding gene (<italic>APX4</italic>) and two thioredoxin (Trx) encoding genes (<italic>TRX2.1</italic> and <italic>TRX2.2</italic>) were up-regulated (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3A, C</bold>
</xref>). Trxs are disulfide reductases containing a conserved active redox center thioredoxin domain (WCGPC), which also exist in GlTRX2.1 and GlTRX2.2 (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S4</bold>
</xref>). Moreover, expression of three genes encoding thioredoxin-like disulfide reductases (TRLs) were up-regulated at 3&#xa0;d after Cd stress (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3A, C</bold>
</xref>). GlTRLs possess a thioredoxin domain and TPR-like_helical domain (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S4</bold>
</xref>), which catalyze the transfer of electrons from a reduced substrate to the disulfide bridge of Trx (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3A</bold>
</xref>). Trxs distribute the reductant to selected targets via a dithiol-disulfide exchange, resulting in the structural and functional modification of a target protein (<xref ref-type="bibr" rid="B4">Balsera and Buchanan, 2019</xref>). Zhang et&#xa0;al. reported that the thioredoxin-like protein CDSP32 improves cadmium tolerance by alleviating Cd-induced photosynthetic inhibition (<xref ref-type="bibr" rid="B51">Zhang et&#xa0;al., 2020</xref>) and modulating antioxidant system in tobacco leaves (<xref ref-type="bibr" rid="B52">Zhang et&#xa0;al., 2023b</xref>).</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>The expression profiles of Cd-responsive genes involved in thioredoxin pathway <bold>(A, C)</bold> and Glutaredoxin cycle, ascorbate-glutathione cycle <bold>(B, C)</bold>. Italics represent genes, red and green represents up-regulation and down- regulation, respectively.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-11-1352529-g003.tif"/>
</fig>
<p>The Glutaredoxin (Grx) cycle, comprised of Grxs, GSH, and glutathione reductase (GR), is crucial for maintaining intracellular redox homeostasis (<xref ref-type="bibr" rid="B27">Ogata et&#xa0;al., 2021</xref>). Grxs are a multifunctional family of glutathione-dependent disulfide oxidoreductases. In <italic>G. lemaneiformis</italic>, expression of Grx encoding gene (<italic>GLX2</italic>) was upregulated at 3&#xa0;d after Cd stress (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3B, C</bold>
</xref>). The ascorbate-glutathione cycle is acknowledged as a cellular redox buffer which donates electrons to various oxidized compounds in plants (<xref ref-type="bibr" rid="B10">Decros et&#xa0;al., 2023</xref>). Expression of genes encoding L-galactose dehydrogenase (GLDH) and glutathione synthetase (GS) was upregulated; these enzymes catalyze the conversion of L-galactose to ascorbate and &#x3b3;-glutamylcysteine to GSH, respectively. Expression levels of <italic>APX</italic>, which detoxifies excess toxic ROS H<sub>2</sub>O<sub>2</sub> to H<sub>2</sub>O, were also upregulated (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3B</bold>
</xref>). These data suggested that the Grx cycle and ascorbate-glutathione cycle alleviates Cd toxicity by scavenging ROS. Glutathione have been proposed as Cd-binding chelator (<xref ref-type="bibr" rid="B35">Sears, 2013</xref>). The upregulation of these genes encoding Trxs, Grxs and GSS showed that sulfur antioxidants may play important roles in controlling oxidative stress in <italic>G. lemaneiformis</italic> exposed to Cd.</p>
</sec>
<sec id="s3_6_3">
<label>3.6.3</label>
<title>DEGs involved in Cd transports</title>
<p>In plants, Cd transporters mainly include natural resistance-associated macrophage protein (Nramp), heavy metal-transporting ATPase (HMA), iron regulated transporter protein (IRT), zinc transporter protein (ZIP), ATP-binding cassette (ABC) and yellow stripe-like (YSL) families (<xref ref-type="bibr" rid="B19">Hu et al., 2022</xref>; <xref ref-type="bibr" rid="B39">Tao and Lu, 2022</xref>). Up to now, Nramps, ZIP5/6/9 and IRT1/2 are found to be involved in the uptake of Cd from the soil to roots in plants (<xref ref-type="bibr" rid="B39">Tao and Lu, 2022</xref>). In <italic>G. lemaneiformis</italic>, YSL transporters do not exist, and the expression of <italic>GlNramps</italic> and <italic>GlHMA</italic> was not altered by Cd. Similarly, <italic>Nramps</italic> were not differentially expressed under Cd stress in algae <italic>C. reinhardti</italic> (<xref ref-type="bibr" rid="B48">Zhang et&#xa0;al., 2023a</xref>). In <italic>G. lemaneiformis</italic>, the expression of transporter genes <italic>GlIRT1</italic> and <italic>GlZIP6</italic> was significantly enhanced by Cd (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>). This suggested that <italic>G. lemaneiformis</italic> actively engages in the uptake and transportation of Cd upon exposure.</p>
<p>Plants possess several detoxification mechanisms to mitigate Cd toxicity including efflux, chelation binding to metallothioneins/PCs and compartmentation to vacuole. In rice, ZIP1, ABCG36 and HMA9 mediate Cd efflux, and ABCG8 mediates Cd efflux in <italic>Arabidopsis thaliana</italic> (<xref ref-type="bibr" rid="B39">Tao and Lu, 2022</xref>). In <italic>G. lemaneiformis</italic>, Cd induced the expression of genes encoding GlZIP1 and GlABCG22 for Cd efflux (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>). Particularly, expression of <italic>GlZIP1</italic> was upregulated more than 2-fold at both 1 and 3&#xa0;d after Cd stress (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>), and that in <italic>C. reinhardti</italic> increased by more than 5 times (<xref ref-type="bibr" rid="B48">Zhang et&#xa0;al., 2023a</xref>). However, expression of genes coding for phytochelatins or metallothioneins did not elevated by Cd. HMA3 and ABCC subfamily transported Cd into vacuole for sequestration in plants (<xref ref-type="bibr" rid="B39">Tao and Lu, 2022</xref>). In <italic>G. lemaneiformis</italic>, the expression of multidrug resistance protein 7 (MRP 7, ABCC subfamily) was significantly upregulated at 3&#xa0;d after Cd stress (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>). Cd is also can bind the dimer of GSH (<xref ref-type="bibr" rid="B53">Zhang et&#xa0;al., 2022b</xref>), which is consistent with the increase of GSH content in our result, and then transported to vacuole in form of chelates. These results indicated that <italic>G. lemaneiformis</italic> through synthesis of GSH, then combined Cd transport into the vacuole and improve Cd efflux to reduce the Cd damage.</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>The DEGs of Cd uptake, efflux and vacuole sequestration genes in response to Cd at 1 and 3&#xa0;d in <italic>G. lemaneiformis</italic>.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-11-1352529-g004.tif"/>
</fig>
</sec>
<sec id="s3_6_4">
<label>3.6.4</label>
<title>Cd negatively affected energy metabolism</title>
<p>KEGG analysis revealed an enrichment of energy metabolism processes, including photosynthesis - antenna proteins and nitrogen metabolism under Cd stress. In the process of photosynthesis - antenna proteins, the genes encoding allophycocyanin (APC), phycocyanin (PC) and light-harvesting chlorophyll protein complex (LHC) were affected under Cd stress (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S5</bold>
</xref>). In total, 27 and 22 transcripts were differentially expressed at 1 and 3&#xa0;d, separately. Of these, 27 and 21 transcripts encoding ApcB-C, CpcA-C, Lhca1 and Lhca4 were down-regulated at 1 and 3&#xa0;d after Cd stress, respectively (<xref ref-type="table" rid="T3">
<bold>Table&#xa0;3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S5</bold>
</xref>). This is consistent with a decrease in photosynthetic pigments PE, PC and Chl a content. In the nitrogen metabolism pathway, 9 (1 up and 8 down) and 13 (4 up and 9 down) transcripts encoding nitrate/nitrite transporter (NRT), nitrate reductase (NAD(P)H), ferredoxin-nitrite reductase, glutamine synthetase, glutamate synthase (ferredoxin) and glutamate dehydrogenase (NAD(P)+) were differentially expressed at 1 and 3&#xa0;d, respectively (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S5</bold>
</xref>). In addition, Cd destroys chloroplast structures, such as the photosynthetic membrane (<xref ref-type="table" rid="T3">
<bold>Table&#xa0;3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S5</bold>
</xref>), which is consistent with results reported in plants (<xref ref-type="bibr" rid="B28">Parmar et&#xa0;al., 2013</xref>). These findings indicated that Cd downregulated the expression of genes involved in the energy metabolism pathway to inhibit the growth of <italic>G. lemaneiformis</italic>.</p>
<table-wrap id="T3" position="float">
<label>Table&#xa0;3</label>
<caption>
<p>The number of DEGs involved in energy metabolism in response to Cd in <italic>G. lemaneiformis</italic>.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="top" rowspan="2" align="left">KEGG pathway</th>
<th valign="top" colspan="2" align="center">Cd vs CK 1d</th>
<th valign="top" colspan="2" align="center">Cd vs CK 3d</th>
</tr>
<tr>
<th valign="top" align="left">up</th>
<th valign="top" align="left">down</th>
<th valign="top" align="left">up</th>
<th valign="top" align="left">down</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Photosynthesis - antenna proteins</td>
<td valign="top" align="left">0</td>
<td valign="top" align="left">27</td>
<td valign="top" align="left">1</td>
<td valign="top" align="left">21</td>
</tr>
<tr>
<td valign="top" align="left">Nitrogen metabolism</td>
<td valign="top" align="left">2</td>
<td valign="top" align="left">9</td>
<td valign="top" align="left">3</td>
<td valign="top" align="left">11</td>
</tr>
<tr>
<td valign="top" align="left">photosynthetic membrane</td>
<td valign="top" align="left">1</td>
<td valign="top" align="left">14</td>
<td valign="top" align="left">0</td>
<td valign="top" align="left">6</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3_6_5">
<label>3.6.5</label>
<title>Transcription factors, G-proteins and heat shock proteins are involved in the response to Cd stress</title>
<p>Many studies have shown that transcription factors are involved in the response to Cd in plants. In <italic>G. lemaneiformis</italic>, most DEGs related to the &#x201c;transcription factor&#x201d; including MYB, TBP-binding protein (TBP) and SNF7 were significantly upregulated under Cd stress, suggesting that TFs participate in response to Cd (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5A</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S6</bold>
</xref>). Among them, 3 transcripts encoding MYB transcription factors were significantly upregulated by Cd at both 1 and 3&#xa0;d. The transcription factor MYBs is one of the most widely distributed families in plants and participate in responses to stresses by binding to the cis-elements of MYB in the promoter of target genes (<xref ref-type="bibr" rid="B42">Wang et&#xa0;al., 2021</xref>). Overexpression of AtMYB4 and SbMYB15 resulted in increased tolerance to Cd (<xref ref-type="bibr" rid="B34">Sapara et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B2">Agarwal et&#xa0;al., 2020</xref>). In addition, &#x201c;G-Protein&#x201d; was also significantly upregulated under Cd stress (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S7</bold>
</xref>). G proteins function as molecular switches to participate in the transmission of various extracellular stimulus signals and responses to abiotic stresses in plants (<xref ref-type="bibr" rid="B50">Zhang et&#xa0;al., 2021</xref>). Studies have shown that overexpression of AGG3 can increase tolerance to Cd (<xref ref-type="bibr" rid="B3">Alvarez et&#xa0;al., 2015</xref>).</p>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>DEGs involved in transcription factors <bold>(A)</bold> and HSPs in response to Cd stress <bold>(B)</bold>.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-11-1352529-g005.tif"/>
</fig>
<p>HSPs act as molecular chaperones for a variety of target proteins in response to heavy metal stress and play a crucial role in maintenance of protein homeostasis (<xref ref-type="bibr" rid="B13">Fragkostefanakis et&#xa0;al., 2015</xref>). In our results, expression of transcripts encoding HSPs including 6 sHsp, 4 Hsp 40, 1 Hsp 90-5 and 1 Hsp 101 was upregulated by Cd (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5B</bold>
</xref>). Particularly, sHSP was greatly induced by Cd, and the multiple was generally between 3-6 times. SHSPs, the first line of stress defense (<xref ref-type="bibr" rid="B16">Haslbeck and Vierling, 2015</xref>), can bind denatured proteins, stabilize them, and prevent an aggregating of denatured proteins without depending on ATP, then the denatured proteins are refolded by either the HSP70 system or the HSP40/HSP70 system (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5B</bold>
</xref>). The highly conserved C-terminal region of sHsp is the &#x3b1;-crystallin domain (ACD domain) (<xref ref-type="bibr" rid="B16">Haslbeck and Vierling, 2015</xref>), which present in all these DEGs of sHsp (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S8</bold>
</xref>). In <italic>Closterium ehrenbergii</italic>, expression of sHSP10 and sHSP17.1 was significantly upregulated under heavy metal stress (<xref ref-type="bibr" rid="B1">Abassi et&#xa0;al., 2019</xref>). Expression of small heat shock protein OsMSR3 in Arabidopsis enhanced tolerance to Cd stress (<xref ref-type="bibr" rid="B8">Cui et&#xa0;al., 2013</xref>). HSP40s together with HSP70s constitute a versatile chaperone machinery for stress responses (<xref ref-type="bibr" rid="B29">Qiu et&#xa0;al., 2006</xref>). However, HSP70s were not induced by Cd in <italic>G. lemaneiformis.</italic> Hsp40 proteins contain the J domain through which they bind to Hsp70s (<xref ref-type="bibr" rid="B29">Qiu et&#xa0;al., 2006</xref>), and the J domain exist in the DEGs of GlHsp40s (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S8</bold>
</xref>). In <italic>Venerupis philippinarum</italic>, the expression of VpHSP40 induced by Cd (<xref ref-type="bibr" rid="B22">Li and Dewey, 2011</xref>) and the Hsp40-like protein provided tolerance to Cd toxicity (<xref ref-type="bibr" rid="B40">Thakur et&#xa0;al., 2021</xref>). Together, these results indicated that HSPs might improve the tolerance to Cd in G. <italic>lemaneiformis.</italic>
</p>
</sec>
</sec>
</sec>
<sec id="s4" sec-type="conclusions">
<label>4</label>
<title>Conclusions</title>
<p>In summary, our work revealed the response of macroalgae to Cd at the molecular level. Both transcriptome and physiological results showed that Cd was toxic to macroalgae and triggered growth and photosynthesis inhibition. Our results showed that ABA levels and the expression of genes related to ABA biosynthesis and signaling pathway was induced in the presence of Cd. And application of ABA alleviated Cd toxicity, suggesting that ABA played a key role against Cd stress in <italic>G. lemaneiformis</italic>. In addition, several ABC and ZIP transporters responding to Cd were identified. Specifically, thioredoxin, glutaredoxin cycle and ascorbate-glutathione cycle played important roles in maintaining ROS homeostasis. Furthermore, MYBs transcription factors, signal transduction factor G-protein and HSPs were involved in detoxification to Cd stress, these genes could be good Cd-responsive marker genes. Taken together, our results identified novel genes and pathways for improving Cd accumulation in algae and provided new insights into the detoxification mechanisms of macroalgae under Cd stress.</p>
</sec>
<sec id="s5" sec-type="data-availability">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Material</bold>
</xref>, further inquiries can be directed to the corresponding author/s.</p>
</sec>
<sec id="s6" sec-type="author-contributions">
<title>Author contributions</title>
<p>XC: Data curation, Visualization, Writing &#x2013; original draft. YT: Methodology, Writing &#x2013; review &amp; editing. XS: Supervision, Writing &#x2013; review &amp; editing. HZ: Software, Writing &#x2013; review &amp; editing. NX: Writing &#x2013; review &amp; editing, Supervision.</p>
</sec>
</body>
<back>
<sec id="s7" sec-type="funding-information">
<title>Funding</title>
<p>The author(s) declare financial support was received for the research, authorship, and/or publication of this article. This study was financially supported by the Natural Science Foundation of Zhejiang Province (LY22C190005), the Natural Science Foundation of China (31901465), and the open fund of the State Key Laboratory of Plant Physiology and Biochemistry (SKLPPBKF2117).</p>
</sec>
<sec id="s8" sec-type="COI-statement">
<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 id="s9" sec-type="disclaimer">
<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 id="s10" sec-type="supplementary-material">
<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/fmars.2024.1352529/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmars.2024.1352529/full#supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="DataSheet_1.xlsx" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.spreadsheetml.sheet"/>
<supplementary-material xlink:href="DataSheet_2.docx" id="SF1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document"/>
</sec>
<ref-list>
<title>References</title>
<ref id="B1">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Abassi</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Ponmani</surname> <given-names>T.</given-names>
</name>
<name>
<surname>Ki</surname> <given-names>J. S.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Small heat shock protein genes of the green algae <italic>Closterium ehrenbergii</italic>: Cloning and differential expression under heat and heavy metal stresses</article-title>. <source>Environ. Toxicol.</source> <volume>34</volume> (<issue>9</issue>), <fpage>1013</fpage>&#x2013;<lpage>1024</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1002/tox.22772</pub-id>
</citation>
</ref>
<ref id="B2">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Agarwal</surname> <given-names>P.</given-names>
</name>
<name>
<surname>Mitra</surname> <given-names>M.</given-names>
</name>
<name>
<surname>Banerjee</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Roy</surname> <given-names>S.</given-names>
</name>
</person-group> (<year>2020</year>). <article-title>MYB4 transcription factor, a member of R2R3-subfamily of MYB domain protein, regulates cadmium tolerance <italic>via</italic> enhanced protection against oxidative damage and increases expression of PCS1 and MT1C in <italic>Arabidopsis</italic>
</article-title>. <source>Plant Sci.</source> <volume>297</volume>, <elocation-id>110501</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.plantsci.2020.110501</pub-id>
</citation>
</ref>
<ref id="B3">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Alvarez</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Roy Choudhury</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Sivagnanam</surname> <given-names>K.</given-names>
</name>
<name>
<surname>Hicks</surname> <given-names>L. M.</given-names>
</name>
<name>
<surname>Pandey</surname> <given-names>S.</given-names>
</name>
</person-group> (<year>2015</year>). <article-title>Quantitative proteomics analysis of <italic>Camelina sativa</italic> seeds overexpressing the AGG3 gene to identify the proteomic basis of increased yield and stress tolerance</article-title>. <source>J. Proteome Res.</source> <volume>14</volume> (<issue>6</issue>), <fpage>2606</fpage>&#x2013;<lpage>2616</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1021/acs.jproteome.5b00150</pub-id>
</citation>
</ref>
<ref id="B4">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Balsera</surname> <given-names>M.</given-names>
</name>
<name>
<surname>Buchanan</surname> <given-names>B. B.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Evolution of the thioredoxin system as a step enabling adaptation to oxidative stress</article-title>. <source>Free Radical Biol. Med.</source> <volume>140</volume>, <fpage>28</fpage>&#x2013;<lpage>35</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.freeradbiomed.2019.03.003</pub-id>
</citation>
</ref>
<ref id="B5">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Chen</surname> <given-names>P.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Luo</surname> <given-names>D.</given-names>
</name>
<name>
<surname>Jia</surname> <given-names>R.</given-names>
</name>
<name>
<surname>Lu</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Tang</surname> <given-names>M.</given-names>
</name>
<etal/>
</person-group>. (<year>2021</year>). <article-title>Comparative transcriptomic analysis reveals key genes and pathways in two different cadmium tolerance kenaf (<italic>Hibiscus cannabinus</italic> L.) cultivars</article-title>. <source>Chemosphere</source> <volume>263</volume>, <elocation-id>128211</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.chemosphere.2020.128211</pub-id>
</citation>
</ref>
<ref id="B6">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Chen</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Tang</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Sun</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Zhang</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Xu</surname> <given-names>N.</given-names>
</name>
</person-group> (<year>2022</year>a). <article-title>Comparative transcriptome analysis reveals the promoting effects of IAA on biomass production and branching of <italic>Gracilariopsis lemaneiformis</italic>
</article-title>. <source>Aquaculture</source> <volume>548</volume>, <elocation-id>737678</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.aquaculture.2021.737678</pub-id>
</citation>
</ref>
<ref id="B7">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Chen</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Tang</surname> <given-names>Y. Y.</given-names>
</name>
<name>
<surname>Yin</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Sun</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Zhang</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Xu</surname> <given-names>N.</given-names>
</name>
</person-group> (<year>2022</year>b). <article-title>A survey of the full-length transcriptome of <italic>Gracilariopsis lemaneiformis</italic> using single-molecule long-read sequencing</article-title>. <source>BMC Plant Biol.</source> <volume>22</volume> (<issue>1</issue>), <fpage>597</fpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1186/s12870-022-03992-0</pub-id>
</citation>
</ref>
<ref id="B8">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Cui</surname> <given-names>Y. C.</given-names>
</name>
<name>
<surname>Xu</surname> <given-names>G. Y.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>M. L.</given-names>
</name>
<name>
<surname>Yu</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>M. J.</given-names>
</name>
<name>
<surname>da Rocha</surname> <given-names>P. S. C. F.</given-names>
</name>
<etal/>
</person-group>. (<year>2013</year>). <article-title>Expression of small heat shock protein OsMSR3 in <italic>Arabidopsis</italic> enhances tolerance to cadmium stress</article-title>. <source>Plant Cell Tissue Organ Cult</source> <volume>113</volume>, <fpage>331</fpage>&#x2013;<lpage>340</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1007/s11240-012-0275-x</pub-id>
</citation>
</ref>
<ref id="B9">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Das</surname> <given-names>U.</given-names>
</name>
<name>
<surname>Rahman</surname> <given-names>M. A.</given-names>
</name>
<name>
<surname>Ela</surname> <given-names>E. J.</given-names>
</name>
<name>
<surname>Lee</surname> <given-names>K. W.</given-names>
</name>
<name>
<surname>Kabir</surname> <given-names>A. H.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Sulfur triggers glutathione and phytochelatin accumulation causing excess Cd bound to the cell wall of roots in alleviating Cd-toxicity in alfalfa</article-title>. <source>Chemosphere</source> <volume>262</volume>, <elocation-id>128361</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.chemosphere.2020.128361</pub-id>
</citation>
</ref>
<ref id="B10">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Decros</surname> <given-names>G.</given-names>
</name>
<name>
<surname>Dussarrat</surname> <given-names>T.</given-names>
</name>
<name>
<surname>Baldet</surname> <given-names>P.</given-names>
</name>
<name>
<surname>Cassan</surname> <given-names>C.</given-names>
</name>
<name>
<surname>Cabasson</surname> <given-names>C.</given-names>
</name>
<name>
<surname>Dieuaide-Noubhani</surname> <given-names>M.</given-names>
</name>
<etal/>
</person-group>. (<year>2023</year>). <article-title>Enzyme-based kinetic modelling of ASC-GSH cycle during tomato fruit development reveals the importance of reducing power and ROS availability</article-title>. <source>New Phytol.</source> <volume>240</volume> (<issue>1</issue>), <fpage>242</fpage>&#x2013;<lpage>257</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1111/nph.19160</pub-id>
</citation>
</ref>
<ref id="B11">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Fang</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Hu</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Yin</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Song</surname> <given-names>G.</given-names>
</name>
<name>
<surname>Cai</surname> <given-names>Q.</given-names>
</name>
</person-group> (<year>2020</year>). <article-title>Exogenous glutathione alleviation of cd toxicity in italian ryegrass (Lolium multiflorum) by modulation of the cd absorption, subcellular distribution, and chemical form</article-title>. <source>Int. J. Environ. Res. Public Health</source> <volume>17</volume> (<issue>21</issue>), <elocation-id>8143</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.3390/ijerph17218143</pub-id>
</citation>
</ref>
<ref id="B12">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Foster</surname> <given-names>P.</given-names>
</name>
</person-group> (<year>1976</year>). <article-title>Concentrations and concentration factors of heavy metals in brown algae</article-title>. <source>Environ. Pollut.</source> <volume>10</volume> (<issue>1</issue>), <fpage>45</fpage>&#x2013;<lpage>53</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/0013-9327(76)90094-x</pub-id>
</citation>
</ref>
<ref id="B13">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Fragkostefanakis</surname> <given-names>S.</given-names>
</name>
<name>
<surname>R&#xf6;th</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Schleiff</surname> <given-names>E.</given-names>
</name>
<name>
<surname>Scharf</surname> <given-names>K. D.</given-names>
</name>
</person-group> (<year>2015</year>). <article-title>Prospects of engineering thermotolerance in crops through modulation of heat stress transcription factor and heat shock protein networks</article-title>. <source>Plant Cell Environ.</source> <volume>38</volume> (<issue>9</issue>), <fpage>1881</fpage>&#x2013;<lpage>1895</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1111/pce.12396</pub-id>
</citation>
</ref>
<ref id="B14">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Gao</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Song</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Zhang</surname> <given-names>F.</given-names>
</name>
<name>
<surname>Yang</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Yang</surname> <given-names>Y.</given-names>
</name>
<etal/>
</person-group>. (<year>2022</year>). <article-title>Response of glutathione pools to cadmium stress and the strategy to translocate cadmium from roots to leaves (Daucus carota L.)</article-title>. <source>Sci. Total Environ.</source> <volume>823</volume>, <elocation-id>153575</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.scitotenv.2022.153575</pub-id>
</citation>
</ref>
<ref id="B15">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Haider</surname> <given-names>F. U.</given-names>
</name>
<name>
<surname>Liqun</surname> <given-names>C.</given-names>
</name>
<name>
<surname>Coulter</surname> <given-names>J. A.</given-names>
</name>
<name>
<surname>Cheema</surname> <given-names>S. A.</given-names>
</name>
<name>
<surname>Wu</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Zhang</surname> <given-names>R.</given-names>
</name>
<etal/>
</person-group>. (<year>2021</year>). <article-title>Cadmium toxicity in plants: Impacts and remediation strategies</article-title>. <source>Ecotoxicol. Environ. Saf.</source> <volume>211</volume>, <elocation-id>111887</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.ecoenv.2020.111887</pub-id>
</citation>
</ref>
<ref id="B16">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Haslbeck</surname> <given-names>M.</given-names>
</name>
<name>
<surname>Vierling</surname> <given-names>E.</given-names>
</name>
</person-group> (<year>2015</year>). <article-title>A first line of stress defense: small heat shock proteins and their function in protein homeostasis</article-title>. <source>J. Mol. Biol.</source> <volume>427</volume> (<issue>7</issue>), <fpage>1537</fpage>&#x2013;<lpage>1548</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.jmb.2015.02.002</pub-id>
</citation>
</ref>
<ref id="B17">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Houessionon</surname> <given-names>M. G. K.</given-names>
</name>
<name>
<surname>Ouendo</surname> <given-names>E. D.</given-names>
</name>
<name>
<surname>Bouland</surname> <given-names>C.</given-names>
</name>
<name>
<surname>Takyi</surname> <given-names>S. A.</given-names>
</name>
<name>
<surname>Kedote</surname> <given-names>N. M.</given-names>
</name>
<name>
<surname>Fayomi</surname> <given-names>B.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Environmental heavy metal contamination from electronic waste (E-waste) recycling activities worldwide: A systematic review from 2005 to 2017</article-title>. <source>Int. J. Environ. Res. Public Health</source> <volume>18</volume> (<issue>7</issue>), <elocation-id>3517</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.3390/ijerph18073517</pub-id>
</citation>
</ref>
<ref id="B18">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Hsu</surname> <given-names>Y. T.</given-names>
</name>
<name>
<surname>Kao</surname> <given-names>C. H.</given-names>
</name>
</person-group> (<year>2003</year>). <article-title>Role of abscisic acid in cadmium tolerance of rice (<italic>Oryza sativa</italic> L.) seedlings</article-title>. <source>Plant Cell Environ.</source> <volume>26</volume> (<issue>6</issue>), <fpage>867</fpage>&#x2013;<lpage>874</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1046/j.1365-3040.2003.01018.x</pub-id>
</citation>
</ref>
<ref id="B19">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Hu</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Chen</surname> <given-names>G.</given-names>
</name>
<name>
<surname>Xu</surname> <given-names>K.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>J.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Cadmium in cereal crops: uptake and transport mechanisms and minimizing strategies</article-title>. <source>J. Agric. Food Chem.</source> <volume>70</volume> (<issue>20</issue>), <fpage>5961</fpage>&#x2013;<lpage>5974</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1021/acs.jafc.1c07896</pub-id>
</citation>
</ref>
<ref id="B20">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ji</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Zou</surname> <given-names>D.</given-names>
</name>
<name>
<surname>Gong</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Liu</surname> <given-names>C.</given-names>
</name>
<name>
<surname>Ye</surname> <given-names>C.</given-names>
</name>
<name>
<surname>Chen</surname> <given-names>Y.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>The different responses of growth and photosynthesis to NH4+ enrichments between Gracilariopsis lemaneiformis and its epiphytic alga Ulva lactuca grown at elevated atmospheric CO2</article-title>. <source>Mar. Pollut. Bull.</source> <volume>144</volume>, <page-range>173&#x2013;180</page-range>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.marpolbul.2019.04.049</pub-id>
</citation>
</ref>
<ref id="B21">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Kumar</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Sharma</surname> <given-names>A.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Cadmium toxicity: effects on human reproduction and fertility</article-title>. <source>Rev. Environ. Health</source> <volume>34</volume> (<issue>4</issue>), <fpage>327</fpage>&#x2013;<lpage>338</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1515/reveh-2019-0016</pub-id>
</citation>
</ref>
<ref id="B22">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Li</surname> <given-names>B.</given-names>
</name>
<name>
<surname>Dewey</surname> <given-names>C. N.</given-names>
</name>
</person-group> (<year>2011</year>). <article-title>RSEM: accurate transcript quantification from RNA-Seq data with or without a reference genome</article-title>. <source>BMC Bioinf.</source> <volume>12</volume>, <elocation-id>323</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1186/1471-2105-12-323</pub-id>
</citation>
</ref>
<ref id="B23">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Livak</surname> <given-names>K. J.</given-names>
</name>
<name>
<surname>Schmittgen</surname> <given-names>T. D.</given-names>
</name>
</person-group> (<year>2001</year>). <article-title>Analysis of relative gene expression data using real-time quantitative PCR and the 2(-&#x394;&#x394; C(T)) Method</article-title>. <source>Methods</source> <volume>25</volume> (<issue>4</issue>), <fpage>402</fpage>&#x2013;<lpage>408</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1006/meth.2001.1262</pub-id>
</citation>
</ref>
<ref id="B24">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Luo</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>Q.</given-names>
</name>
<name>
<surname>Liu</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Long</surname> <given-names>A.</given-names>
</name>
<name>
<surname>Yang</surname> <given-names>Y.</given-names>
</name>
</person-group> (<year>2020</year>). <article-title>Potential bioremediation effects of seaweed <italic>Gracilaria lemaneiformis</italic> on heavy metals in coastal sediment from a typical mariculture zone</article-title>. <source>Chemosphere</source> <volume>245</volume>, <elocation-id>125636</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.chemosphere.2019.125636</pub-id>
</citation>
</ref>
<ref id="B25">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Luo</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>Q.</given-names>
</name>
<name>
<surname>Zhang</surname> <given-names>C.</given-names>
</name>
<name>
<surname>Zhang</surname> <given-names>L.</given-names>
</name>
<name>
<surname>Yang</surname> <given-names>Y.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Bioaccumulation and release of heavy metals during growth and decomposition of cultivated <italic>Gracilaria lemaneiformis</italic>
</article-title>. <source>Mar. Pollut. Bull.</source> <volume>173</volume> (<issue>Pt B</issue>), <elocation-id>113130</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.marpolbul.2021.113130</pub-id>
</citation>
</ref>
<ref id="B26">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Meng</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Huang</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Jing</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Wu</surname> <given-names>Q.</given-names>
</name>
<name>
<surname>Shen</surname> <given-names>R.</given-names>
</name>
<name>
<surname>Zhu</surname> <given-names>X.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Exogenous abscisic acid alleviates Cd toxicity in <italic>Arabidopsis thaliana</italic> by inhibiting Cd uptake, translocation and accumulation, and promoting Cd chelation and efflux</article-title>. <source>Plant Sci.</source> <volume>325</volume>, <elocation-id>111464</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.plantsci.2022.111464</pub-id>
</citation>
</ref>
<ref id="B27">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ogata</surname> <given-names>F. T.</given-names>
</name>
<name>
<surname>Branco</surname> <given-names>V.</given-names>
</name>
<name>
<surname>Vale</surname> <given-names>F. F.</given-names>
</name>
<name>
<surname>Coppo</surname> <given-names>L.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Glutaredoxin: Discovery, redox defense and much more</article-title>. <source>Redox Biol.</source> <volume>43</volume>, <elocation-id>101975</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.redox.2021.101975</pub-id>
</citation>
</ref>
<ref id="B28">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Parmar</surname> <given-names>P.</given-names>
</name>
<name>
<surname>Kumari</surname> <given-names>N.</given-names>
</name>
<name>
<surname>Sharma</surname> <given-names>V.</given-names>
</name>
</person-group> (<year>2013</year>). <article-title>Structural and functional alterations in photosynthetic apparatus of plants under cadmium stress</article-title>. <source>Botanical Stud.</source> <volume>54</volume> (<issue>1</issue>), <elocation-id>45</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1186/1999-3110-54-45</pub-id>
</citation>
</ref>
<ref id="B29">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Qiu</surname> <given-names>X. B.</given-names>
</name>
<name>
<surname>Shao</surname> <given-names>Y. M.</given-names>
</name>
<name>
<surname>Miao</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>L.</given-names>
</name>
</person-group> (<year>2006</year>). <article-title>The diversity of the DnaJ/Hsp40 family, the crucial partners for Hsp70 chaperones</article-title>. <source>Cell. Mol. Life Sci.</source> <volume>63</volume> (<issue>22</issue>), <fpage>2560</fpage>&#x2013;<lpage>2570</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1007/s00018-006-6192-6</pub-id>
</citation>
</ref>
<ref id="B30">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Rahman</surname> <given-names>S. U.</given-names>
</name>
<name>
<surname>Nawaz</surname> <given-names>M. F.</given-names>
</name>
<name>
<surname>Gul</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Yasin</surname> <given-names>G.</given-names>
</name>
<name>
<surname>Hussain</surname> <given-names>B.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>Y.</given-names>
</name>
<etal/>
</person-group>. (<year>2022</year>). <article-title>State-of-the-art OMICS strategies against toxic effects of heavy metals in plants: A review</article-title>. <source>Ecotoxicol. Environ. Saf.</source> <volume>242</volume>, <elocation-id>113952</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.ecoenv.2022.113952</pub-id>
</citation>
</ref>
<ref id="B31">
<citation citation-type="book">
<person-group person-group-type="author">
<name>
<surname>Ramegowda</surname> <given-names>V.</given-names>
</name>
<name>
<surname>Da Costa</surname> <given-names>M. V. J.</given-names>
</name>
<name>
<surname>Harihar</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Karaba</surname> <given-names>N. N.</given-names>
</name>
<name>
<surname>Sreeman</surname> <given-names>S. M.</given-names>
</name>
</person-group> (<year>2020</year>). &#x201c;<article-title>Abiotic and biotic stress interactions in plants: a cross-tolerance perspective</article-title>,&#x201d; in <source>Priming-Mediated Stress and Cross-stress Tolerance in Crop Plants</source> (<publisher-loc>Amsterdam</publisher-loc>: <publisher-name>Elsevier</publisher-name>), <fpage>267</fpage>&#x2013;<lpage>302</lpage>.</citation>
</ref>
<ref id="B32">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Rasafi</surname> <given-names>T. E.</given-names>
</name>
<name>
<surname>Oukarroum</surname> <given-names>A.</given-names>
</name>
<name>
<surname>Haddioui</surname> <given-names>A.</given-names>
</name>
<name>
<surname>Song</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Rinklebe</surname> <given-names>J.</given-names>
</name>
</person-group> (<year>2020</year>). <article-title>Cadmium stress in plants: a critical review of the effects, mechanisms, and tolerance strategies</article-title>. <source>Environ. Sci. Technol.</source> <volume>52</volume> (<issue>5</issue>), <fpage>675</fpage>&#x2013;<lpage>726</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1080/10643389.2020.1835435</pub-id>
</citation>
</ref>
<ref id="B33">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Sampath-Wiley</surname> <given-names>P.</given-names>
</name>
<name>
<surname>Neefus</surname> <given-names>C. D.</given-names>
</name>
</person-group> (<year>2007</year>). <article-title>An improved method for estimating R-phycoerythrin and R-phycocyanin contents from crude aqueous extracts of <italic>Porphyra</italic> (Bangiales, Rhodophyta)</article-title>. <source>J. Appl. Phycol.</source> <volume>19</volume> (<issue>2</issue>), <fpage>123</fpage>&#x2013;<lpage>129</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1007/s10811-006-9118-7</pub-id>
</citation>
</ref>
<ref id="B34">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Sapara</surname> <given-names>K. K.</given-names>
</name>
<name>
<surname>Khedia</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Agarwal</surname> <given-names>P.</given-names>
</name>
<name>
<surname>Gangapur</surname> <given-names>D. R.</given-names>
</name>
<name>
<surname>Agarwal</surname> <given-names>P. K.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>SbMYB15 transcription factor mitigates cadmium and nickel stress in transgenic tobacco by limiting uptake and modulating antioxidative defence system</article-title>. <source>Funct. Plant Biol.</source> <volume>46</volume> (<issue>8</issue>), <fpage>702</fpage>&#x2013;<lpage>714</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1071/FP18234</pub-id>
</citation>
</ref>
<ref id="B35">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Sears</surname> <given-names>M. E.</given-names>
</name>
</person-group> (<year>2013</year>). <article-title>Chelation: harnessing and enhancing heavy metal detoxification&#x2013;a review</article-title>. <source>Sci. World J.</source> <volume>219840</volume>, <fpage>1</fpage>&#x2013;<lpage>13</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1155/2013/219840</pub-id>
</citation>
</ref>
<ref id="B36">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Shao</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Zhou</surname> <given-names>H. Z.</given-names>
</name>
<name>
<surname>Wu</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Zhang</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Lin</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Jiang</surname> <given-names>X.</given-names>
</name>
<etal/>
</person-group>. (<year>2019</year>). <article-title>OsSPL3, an SBP-domain protein, regulates crown root development in rice</article-title>. <source>Plant Cell</source> <volume>31</volume> (<issue>6</issue>), <fpage>1257</fpage>&#x2013;<lpage>1275</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1105/tpc.19.00038</pub-id>
</citation>
</ref>
<ref id="B37">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Smiri</surname> <given-names>M.</given-names>
</name>
<name>
<surname>Chaoui</surname> <given-names>A.</given-names>
</name>
<name>
<surname>Rouhier</surname> <given-names>N.</given-names>
</name>
<name>
<surname>Gelhaye</surname> <given-names>E.</given-names>
</name>
<name>
<surname>Jacquot</surname> <given-names>J. P.</given-names>
</name>
<name>
<surname>El Ferjani</surname> <given-names>E.</given-names>
</name>
</person-group> (<year>2011</year>). <article-title>Cadmium affects the glutathione/glutaredoxin system in germinating pea seeds</article-title>. <source>Biol. Trace element Res.</source> <volume>142</volume> (<issue>1</issue>), <fpage>93</fpage>&#x2013;<lpage>105</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1007/s12011-010-8749-3</pub-id>
</citation>
</ref>
<ref id="B38">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Tang</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>L.</given-names>
</name>
<name>
<surname>Xie</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Yu</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Lin</surname> <given-names>L.</given-names>
</name>
<etal/>
</person-group>. (<year>2020</year>). <article-title>Effects of exogenous abscisic acid on the growth and cadmium accumulation of lettuce under cadmium-stress conditions</article-title>. <source>Int. J. Environ. Anal. Chem.</source> <volume>100</volume> (<issue>6</issue>), <fpage>720</fpage>&#x2013;<lpage>731</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1080/03067319.2019.1639686</pub-id>
</citation>
</ref>
<ref id="B39">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Tao</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Lu</surname> <given-names>L.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Advances in genes-encoding transporters for cadmium uptake, translocation, and accumulation in plants</article-title>. <source>Toxics</source> <volume>10</volume> (<issue>8</issue>), <elocation-id>411</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.3390/toxics10080411</pub-id>
</citation>
</ref>
<ref id="B40">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Thakur</surname> <given-names>B.</given-names>
</name>
<name>
<surname>Yadav</surname> <given-names>R.</given-names>
</name>
<name>
<surname>Mukherjee</surname> <given-names>A.</given-names>
</name>
<name>
<surname>Melayah</surname> <given-names>D.</given-names>
</name>
<name>
<surname>Marmeisse</surname> <given-names>R.</given-names>
</name>
<name>
<surname>Fraissinet-Tachet</surname> <given-names>L.</given-names>
</name>
<etal/>
</person-group>. (<year>2021</year>). <article-title>Protection from metal toxicity by Hsp40-like protein isolated from contaminated soil using functional metagenomic approach</article-title>. <source>Environ. Sci. Pollut. Res. Int.</source> <volume>28</volume> (<issue>14</issue>), <fpage>17132</fpage>&#x2013;<lpage>17145</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1007/s11356-020-12152-6</pub-id>
</citation>
</ref>
<ref id="B41">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wang</surname> <given-names>P. L.</given-names>
</name>
<name>
<surname>Lei</surname> <given-names>X. J.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>Y. Y.</given-names>
</name>
<name>
<surname>Liu</surname> <given-names>B. C.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>D. N.</given-names>
</name>
<name>
<surname>Liu</surname> <given-names>Z. Y.</given-names>
</name>
<etal/>
</person-group>. (<year>2022</year>). <article-title>Transcriptomic analysis of cadmium stressed <italic>tamarix hispida</italic> revealed novel transcripts and the importance of abscisic acid network</article-title>. <source>Front. Plant Sci.</source> <volume>13</volume>. doi:&#xa0;<pub-id pub-id-type="doi">10.3389/fpls.2022.843725</pub-id>
</citation>
</ref>
<ref id="B42">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wang</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Niu</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Zheng</surname> <given-names>Y.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Multiple functions of MYB transcription factors in abiotic stress responses</article-title>. <source>Int. J. Mol. Sci.</source> <volume>22</volume> (<issue>11</issue>), <elocation-id>6125</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.3390/ijms22116125</pub-id>
</citation>
</ref>
<ref id="B43">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wang</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Ke</surname> <given-names>C.</given-names>
</name>
</person-group> (<year>2014</year>). <article-title>Bioaccumulation of trace metals by the live macroalga <italic>Gracilaria lemaneiformis</italic>
</article-title>. <source>J. Appl. Phycol.</source> <volume>26</volume> (<issue>4</issue>), <fpage>1889</fpage>&#x2013;<lpage>1897</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1007/s10811-013-0222-1</pub-id>
</citation>
</ref>
<ref id="B44">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Xia</surname> <given-names>J. R.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>Y. J.</given-names>
</name>
<name>
<surname>Lu</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Chen</surname> <given-names>B.</given-names>
</name>
</person-group> (<year>2004</year>). <article-title>Effects of copper and cadmium on growth, photosynthesis, and pigment content in <italic>Gracilaria lemaneiformis</italic>
</article-title>. <source>Bull. Environ. Contamination Toxicol.</source> <volume>73</volume> (<issue>6</issue>), <fpage>979</fpage>&#x2013;<lpage>986</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1007/s00128-004-0522-x</pub-id>
</citation>
</ref>
<ref id="B45">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Xiao</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Shahab</surname> <given-names>A.</given-names>
</name>
<name>
<surname>Ye</surname> <given-names>F.</given-names>
</name>
<name>
<surname>Wei</surname> <given-names>G.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Deng</surname> <given-names>L.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Source-specific ecological risk assessment and quantitative source apportionment of heavy metals in surface sediments of Pearl River Estuary, China</article-title>. <source>Mar. Pollut. Bull.</source> <volume>179</volume>, <elocation-id>113726</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.marpolbul.2022.113726</pub-id>
</citation>
</ref>
<ref id="B46">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Yu</surname> <given-names>C.</given-names>
</name>
<name>
<surname>Sui</surname> <given-names>W.</given-names>
</name>
<name>
<surname>Liang</surname> <given-names>B.</given-names>
</name>
<name>
<surname>Bao</surname> <given-names>C.</given-names>
</name>
<name>
<surname>Ma</surname> <given-names>M.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Temporal trends of heavy metals in the sediments of Bohai Bay in China</article-title>. <source>Environ. Monit. Assess.</source> <volume>194</volume> (<issue>2</issue>), <fpage>79</fpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1007/s10661-021-09747-y</pub-id>
</citation>
</ref>
<ref id="B47">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Yu</surname> <given-names>M.</given-names>
</name>
<name>
<surname>Zhuo</surname> <given-names>R.</given-names>
</name>
<name>
<surname>Lu</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Chen</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>Y.</given-names>
</name>
<etal/>
</person-group>. (<year>2023</year>). <article-title>Molecular insights into lignin biosynthesis on cadmium tolerance: Morphology, transcriptome and proteome profiling in <italic>Salix matSudana</italic>
</article-title>. <source>J. Hazard. Mater.</source> <volume>441</volume>, <elocation-id>129909</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.jhazmat.2022.129909</pub-id>
</citation>
</ref>
<ref id="B48">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhang</surname> <given-names>B.</given-names>
</name>
<name>
<surname>Tang</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Yu</surname> <given-names>F.</given-names>
</name>
<name>
<surname>Peng</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Yao</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Deng</surname> <given-names>X.</given-names>
</name>
<etal/>
</person-group>. (<year>2023</year>a). <article-title>Translatomics and physiological analyses of the detoxification mechanism of green alga <italic>Chlamydomonas reinhardtii</italic> to cadmium toxicity</article-title>. <source>J. Hazard. Mater.</source> <volume>448</volume>, <elocation-id>130990</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.jhazmat.2023.130990</pub-id>
</citation>
</ref>
<ref id="B49">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhang</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Reynolds</surname> <given-names>M.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Cadmium exposure in living organisms: A short review</article-title>. <source>Sci. Total Environ.</source> <volume>678</volume>, <page-range>761&#x2013;767</page-range>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.scitotenv.2019.04.395</pub-id>
</citation>
</ref>
<ref id="B50">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhang</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Xie</surname> <given-names>P.</given-names>
</name>
<name>
<surname>Xu</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Xie</surname> <given-names>Q.</given-names>
</name>
<name>
<surname>Yu</surname> <given-names>F.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Heterotrimeric G protein signalling in plant biotic and abiotic stress response</article-title>. <source>Plant Biol. (Stuttgart Germany)</source> <volume>23</volume> (<supplement>Suppl 1</supplement>), <fpage>20</fpage>&#x2013;<lpage>30</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1111/plb.13241</pub-id>
</citation>
</ref>
<ref id="B51">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhang</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Xu</surname> <given-names>Z.</given-names>
</name>
<name>
<surname>Huo</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Guo</surname> <given-names>K.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>He</surname> <given-names>G.</given-names>
</name>
<etal/>
</person-group>. (<year>2020</year>). <article-title>Overexpression of Trx CDSP32 gene promotes chlorophyll synthesis and photosynthetic electron transfer and alleviates cadmium-induced photoinhibition of PSII and PSI in tobacco leaves</article-title>. <source>J. Hazard. Mater.</source> <volume>398</volume>, <elocation-id>122899</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.jhazmat.2020.122899</pub-id>
</citation>
</ref>
<ref id="B52">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhang</surname> <given-names>H.</given-names>
</name>
<name>
<surname>Yao</surname> <given-names>T.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Wang</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Song</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Cui</surname> <given-names>C.</given-names>
</name>
<etal/>
</person-group>. (<year>2023</year>b). <article-title>Trx CDSP32-overexpressing tobacco plants improves cadmium tolerance by modulating antioxidant mechanism</article-title>. <source>Plant Physiol. Biochem.</source> <volume>194</volume>, <fpage>524</fpage>&#x2013;<lpage>532</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.plaphy.2022.11.036</pub-id>
</citation>
</ref>
<ref id="B53">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhang</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Zhu</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Yu</surname> <given-names>L.</given-names>
</name>
<name>
<surname>Yang</surname> <given-names>M.</given-names>
</name>
<name>
<surname>Zou</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Yin</surname> <given-names>C.</given-names>
</name>
<etal/>
</person-group>. (<year>2022</year>b). <article-title>Research advances in cadmium uptake, transport and resistance in rice (<italic>Oryza sativa</italic> L.)</article-title>. <source>Cells</source> <volume>11</volume> (<issue>3</issue>), <elocation-id>569</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.3390/cells11030569</pub-id>
</citation>
</ref>
<ref id="B54">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhang</surname> <given-names>M.</given-names>
</name>
<name>
<surname>Sun</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Hu</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Chen</surname> <given-names>G.</given-names>
</name>
<name>
<surname>Xu</surname> <given-names>J.</given-names>
</name>
</person-group> (<year>2022</year>a). <article-title>The influence of anthropogenic activities on heavy metal pollution of estuary sediment from the coastal East China Sea in the past nearly 50 years</article-title>. <source>Mar. Pollut. Bull.</source> <volume>181</volume>, <elocation-id>113872</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.marpolbul.2022.113872</pub-id>
</citation>
</ref>
<ref id="B55">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhao</surname> <given-names>K.</given-names>
</name>
<name>
<surname>Bao</surname> <given-names>K.</given-names>
</name>
<name>
<surname>Yan</surname> <given-names>Y.</given-names>
</name>
<name>
<surname>Neupane</surname> <given-names>B.</given-names>
</name>
<name>
<surname>Gao</surname> <given-names>C.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Spatial distribution of potentially harmful trace elements and ecological risk assessment in Zhanjiang mangrove wetland, South China</article-title>. <source>Mar. Pollut. Bull.</source> <volume>182</volume>, <elocation-id>114033</elocation-id>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.marpolbul.2022.114033</pub-id>
</citation>
</ref>
<ref id="B56">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhu</surname> <given-names>D.</given-names>
</name>
<name>
<surname>Wen</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>S.</given-names>
</name>
<name>
<surname>Xuan</surname> <given-names>X.</given-names>
</name>
<name>
<surname>Li</surname> <given-names>Y.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>Evaluation of the red alga <italic>Gracilaria lemaneiformis</italic> and brown alga <italic>Sargassum horneri</italic> as ingredients in diets for white spotted snapper Lutjanus <italic>stellatus Akazaki</italic> juveniles</article-title>. <source>J. Appl. Phycol.</source> <volume>29</volume>, <fpage>3211</fpage>&#x2013;<lpage>3219</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1007/s10811-017-1187-2</pub-id>
</citation>
</ref>
<ref id="B57">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zou</surname> <given-names>D.</given-names>
</name>
<name>
<surname>Gao</surname> <given-names>K.</given-names>
</name>
</person-group> (<year>2014</year>). <article-title>Temperature response of photosynthetic light- and carbon-use characteristics in the red seaweed <italic>Gracilariopsis lemaneiformis</italic> (<italic>Gracilariales</italic>, Rhodophyta)</article-title>. <source>J. Phycol.</source> <volume>50</volume> (<issue>2</issue>), <fpage>366</fpage>&#x2013;<lpage>375</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1111/jpy.12171</pub-id>
</citation>
</ref>
<ref id="B58">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zou</surname> <given-names>D.</given-names>
</name>
<name>
<surname>Xia</surname> <given-names>J.</given-names>
</name>
<name>
<surname>Yang</surname> <given-names>Y.</given-names>
</name>
</person-group> (<year>2004</year>). <article-title>Photosynthetic use of exogenous inorganic carbon in the agarophyte <italic>Gracilaria lemaneiformis</italic> (Rhodophyta)</article-title>. <source>Aquaculture</source> <volume>237</volume> (<issue>1-4</issue>), <fpage>421</fpage>&#x2013;<lpage>431</lpage>. doi:&#xa0;<pub-id pub-id-type="doi">10.1016/j.aquaculture.2004.04.020</pub-id>
</citation>
</ref>
</ref-list>
</back>
</article>