Skip to main content
Advertisement
Browse Subject Areas
?

Click through the PLOS taxonomy to find articles in your field.

For more information about PLOS Subject Areas, click here.

  • Loading metrics

Gene expression profiling of Jack Pine (Pinus banksiana) under copper stress: Identification of genes associated with copper resistance

  • Alistar Moy,

    Roles Formal analysis, Investigation, Methodology, Validation, Writing – original draft

    Affiliation Biomolecular Sciences Program, School of Natural Sciences, Laurentian University, Sudbury, Ontario, Canada

  • Karolina Czajka,

    Roles Formal analysis, Methodology, Validation

    Affiliation Biomolecular Sciences Program, School of Natural Sciences, Laurentian University, Sudbury, Ontario, Canada

  • Paul Michael,

    Roles Conceptualization, Methodology, Validation, Writing – review & editing

    Affiliation Biomolecular Sciences Program, School of Natural Sciences, Laurentian University, Sudbury, Ontario, Canada

  • Kabwe Nkongolo

    Roles Conceptualization, Funding acquisition, Methodology, Resources, Supervision, Validation, Writing – review & editing

    knkongolo@laurentian.ca

    Affiliations Biomolecular Sciences Program, School of Natural Sciences, Laurentian University, Sudbury, Ontario, Canada, Department of Biology, School of Natural Sciences, Laurentian University, Sudbury, Ontario, Canada

Abstract

Understanding the genetic response of plants to copper stress is a necessary step to improving the utility of plants for environmental remediation and restoration. The objectives of this study were to: 1) characterize the transcriptome of Jack Pine (Pinus banksiana) under copper stress, 2) analyze the gene expression profile shifts of genotypes exposed to copper ion toxicity, and 3) identify genes associated with copper resistance. Pinus banksiana seedlings were treated with 10 mmoles of copper and screened in a growth chamber. There were 6,213 upregulated and 29,038 downregulated genes expressed in the copper resistant genotypes compared to the susceptible genotypes at a high stringency based on the false discovery rate (FDR). Overall, 25,552 transcripts were assigned gene ontology. Among the top upregulated genes, the response to stress, the biosynthetic process, and the response to chemical stimuli terms represented the highest proportion of gene expression for the biological processes. For the molecular function category, the majority of expressed genes were associated with nucleotide binding followed by transporter activity, and kinase activity. The majority of upregulated genes were located in the plasma membrane while half of the total downregulated genes were associated with the extracellular region. Two candidate genes associated with copper resistance were identified including genes encoding for heavy metal-associated isoprenylated plant proteins (AtHIP20 and AtHIP26) and a gene encoding the pleiotropic drug resistance protein 1 (NtPDR1). This study represents the first report of transcriptomic responses of a conifer species to copper ions.

Introduction

Understanding plant resistance to copper is an important step to efficiently revitalize areas afflicted by mining and industrial pollution. Plant resistance to copper is especially important for areas that are poised to increase copper production and exportation. Many facets of plant development and physiology are reliant on copper and the role it plays as an essential ion. Proteins that utilize copper are associated with photosynthesis, cellular respiration, cell wall fortification, growth modulation, apoptosis, and antioxidative functions [14]. An excess of copper causes a variety of symptoms that may damage tissues and impede development. Excess of copper in root cells, competitively inhibits the uptake of essential ions such as iron, manganese, and zinc resulting in disturbed ion homeostasis [57]. It can replace iron in the binding site of plastoquinone QA of Photosystem II, leading to diminished electron transfer during photosynthesis [8]. Copper toxicity leads to decreased chlorophyll and thylakoid membranes content, which impedes photosynthesis and contribute to chlorosis [9]. Decreased nitric oxide production is another symptom of copper toxicity that results in diminished auxin production, cytokinin activity, and mitotic activity in root cells. ROS production induced by copper may also lead to oxidative stress, lipid peroxidation, plant tissue damage and organelle death [1013].

The genetic and physiological bases of copper resistance have been partially described in the literature. In Arabidopsis thaliana, the downregulation of COPT1, COPT2, ZIP2 and ZIP4 indicate a decrease in the initial uptake of copper into the root cells [1416]. Upregulation of the HMA5 transporter in Arabidopsis thaliana and Oryza sativa suggests an increased copper mobilization in roots and also an increased root to shoot Cu translocation [15, 17, 18]. An upregulation of HMA1 and HMA6/PAA1 transporters in Arabidopsis thaliana, suggests an increased of root to shoot Cu translocation and its transport to chloroplasts [15, 19, 20]. The HMA8/PAA2 transporter was also upregulated, demonstrating the increased transport of copper to the thylakoid lumen and plastocyanin [15, 21, 22]. Collectively, the higher amount of Cu delivery to the chloroplast stroma, thylakoid lumen and plastocyanin may suggest increased photosynthesis [22, 23]. Similarly, the increased expression of AtHMA7 encourages copper transport to the Golgi apparatus and ethylene receptors located in the ER, suggesting an enhanced growth to counteract Cu toxicity symptoms [24]. The OsHMA9 gene was upregulated in the xylem and phloem of Oryza sativa exposed to Cu indicating an increased xylem and phloem loading [20]. Genes encoding the chelators MT2a and MT2b were upregulated in root tips, shoots, and phloem area which indicated an elevated metallothionein production for copper chelation in those respective areas [25, 26].

Currently, the response of conifers to metals are elusive and under researched in comparison to angiosperms. Transcriptome analysis of copper resistant trees will be a valuable tool to uncover physiological mechanisms associated with copper resistance or tolerance. Pinus banksiana was selected as a candidate for transcriptome analysis due to its successful utilization in the Sudbury regreening program [2729]. In addition to being a hardy and resilient tree, Pinus banksiana was observed to have a moderate genetic diversity and low gene flow in metal contaminated sites [30, 31]. Furthermore, newer population of Pinus banksiana that were used in the regreening program had a significantly higher genetic diversity in comparison to older populations.

The objectives of this study were to: 1) characterize the transcriptome of Jack Pine (Pinus banksiana) under copper stress, 2) analyze the gene expression variation in genotypes exposed to copper ion toxicity and 3) identify genes associated with copper resistance.

Materials and methods

Plant treatment

Pinus banksiana seedings were provided by the College Boreal Plant Center located in Sudbury, Ontario. Six-month old seedlings of Pinus banksiana were grown in growth chambers at Laurentian University according to the methodology outlined in Moarefi and Nkongolo (2022) [32]. Initially, they were transplanted into planter pots containing a 1:1 mixture of sand and a mixture of 79% Sphagmum moss, 17% perlite, 5% composted peatmoss. The seedlings were then incubated in a growth chamber for one month. They were fertilized with a 1:1:1 mixture of nitrogen, phosphorous, and potassium fertilizer when required. After this one month period, fifteen seedlings were treated with 1,300 mg of copper sulphate per 1 kg of soil (10 mmol of Cu). This treatment represented the in field concentration of Cu from a survey on metal contaminated sites in the Greater Sudbury Region [29]. Ten seedlings were treated with deionized water that represented the negative control. Ten seedlings were treated with a molar equivalent of potassium sulphate relative to copper sulphate with respect to the sulphate ions. Damages were measured 14 days after treatment using a 1 to 9 scale, 1 indicating no damage and 9 indicating dead plants as described in Moarefi and Nkongolo (2022) [32]. Details of the rating scale is described in S1 Table in S1 File. Needles from resistant genotypes with no symptoms and green needles from susceptible genotypes were harvested and wrapped in individual aluminum foils for RNA extraction. For longer term storage, the needles were flash frozen using liquid nitrogen and stored in a freezer at -80°C.

RNA extraction

Transcriptome analysis was performed on three plants (3 replicates) for each treatment (copper sulfate, potassium sulfate, and water) and for each type of the genotypes (resistant and susceptible). RNA extraction was performed on the green needles of the seedlings following the protocol from the NORGEN BIOTEK Plant/fungi total RNA purification Kit https://norgenbiotek.com/product/plantfungi-total-rna-purification-kit. Agarose gel electrophoresis was performed on the extracted RNA to assess RNA quality. The quantity of RNA for each sample was determined using the Qubit™ RNA BR assay kit. The extracted RNA samples were stored in a freezer at -80°C.

RNA sequencing and de novo transcriptome assembly

Messenger RNA (mRNA) was isolated from total RNA. RNA chemical fragmentation was done to account for the size limitation of the sequencing platform. Then, this mRNA was reverse transcribed to cDNA using reverse transcriptase and RNAse was added to prevent unnecessary ligation between different nucleotide strands. Second strand synthesis was performed followed by 3’ end ligation with adaptors and adenosine caps. The cDNA was amplified to generate cDNA libraries. Illumina sequencing (performed at Seqmatic in San Francisco, California, USA) was used to sequence the cDNA libraries. FASTQC files containing the raw reads of each cDNA library was generated for each sample. The FASTQC program verified the quality of raw data from the files and provided attributes for each sequence which included average sequence length, % GC content, total deduplicated percentage and sequences flagged as poor quality. The Cutadapt program was used to remove adaptor sequences and low-quality bases from the raw read data. The Bowtie2 algorithm in Trinity was used to map RNA sequence raw reads to the trinity transcript assembly, generating sequence alignment map (SAM) files which were then converted to BAM (binary form of SAM) files. Transcript assembly was performed by inputting RNA sequence data from all samples into the TRINITY program, which quantified the number of genes based on the number of detected isoforms.

BLAT matching and annotation of Pinus banksiana genes

Transcripts were characterized by performing a two-way BLAST-like alignment tool (BLAT) matching with the Pinus taeda genome as a reference. Attributes such as Transcript ID, Gene ID, and corresponding log (E-value) for sequence similarity with the reference genome was characterized. Other characteristics identified by BLAT matching include query sequence size, transcript sequence size, and the percentage of net match for each characteristic. Transcripts were mapped to protein sequences in the UniProt database, generating corresponding UniProt IDs. Protein matches with the highest degree of similarity were used to annotate genes and assign gene ontology information such as gene description.

Quantification of gene expression and quality control (QC) analysis

The RNA-Seq by Expectation-Maximization (RSEM) abundance estimation method was used to quantify the expression level of each gene/transcript and related isoforms. Quality control for read count was performed to critically assess the number of counts from each gene. Raw reads were filtered and selected for counts of at least 1, 2, 10, 50 or 100. Genes with one read were considered noise. Genes with two or more counts were used as an estimate for the number of genes expressed. Genes with 10 or more counts were considered an adequate indication of the number of genes that had enough reads for downstream statistical analysis. For each treatment group, genes with a counts per million (CPM) value of 1 or higher in at least 2 samples were included in downstream analysis. Genes with a CPM value of less than 1 in at least 2 samples were unexpressed and removed. Normalization factors for raw counts were generated using a trimmed mean of M-values (TMM) from edge R to remove variations from samples and normalize the samples.

The normalized read counts were log-scale transformed using the voom method (log2 scale) from the R limma package. Boxplots of the transformed expression values were generated to show the mean distribution of every sample. Deviation from the mean distribution in a particular sample may indicate variations among experimental conditions, sample contamination or batch effect. Samples that deviated significantly from the mean distribution within the same objective group were excluded.

Multidimensional scaling plots were generated to display the clustering of sample groups based on the leading logFC of normalized data. Groups of samples that deviated significantly from other groups of samples were considered differentially regulated. Samples that deviated significantly from the other samples within the same group were considered outliers and not included in downstream analysis.

A heatmap was generated from the logFC of 5000 genes to show the relationship of gene expression between the samples. Samples that did not have a similar logFC were considered outliers and were not included in downstream analysis. The proportion of raw reads expressed by the top 100 upregulated and downregulated genes were also assessed in every sample to identify potential bottlenecking issues.

Differential gene expression (DGE) analysis of pairwise comparisons

The cut-off for pairwise comparisons was calculated to be equivalent to 10 raw counts. From the average of total counts in all samples, a CPM of 0.361 was calculated as the minimum threshold required in pairwise comparisons. Genes that had a CPM higher than the cutoff in at least two samples were included in downstream analysis whereas genes that did not fulfill these parameters were excluded. The pairwise comparisons of transcripts were performed between treated samples and the control. Differential gene expression expressed as logFC values were evaluated using the R limma package. To assess the interference of sulphate ions on the treatment regimen, pairwise comparisons of expressed genes were also conducted between copper treated plants and the potassium and water used as controls. The entire set of genes for each pairwise comparison was annotated using Trinotate and Trinity. Gene ontology was performed by assigning GO terms and gene IDs from available databases to the set of genes for a particular pairwise comparison. Genes that could not be annotated were filtered out of the set of annotated genes. Each gene set was run through a plant slim function using the Omicsbox program. Gene ontology charts functionally categorizing biological process, metabolic function, and cellular component were generated. For each functional category, sequences were distributed using the NodeScore of each assigned GO term.

Analysis of top differentially regulated genes

The top 100 upregulated and downregulated genes were ranked between copper treated plants and the control. Genes were ranked based on the LogFC and the fulfillment of high stringency parameters. UniProt annotation and review of the current literature was done to characterize genes associated with copper detoxification tolerance mechanisms. Genes associated with copper resistance were considered candidate genes. Gene ontology charts functionally categorizing biological processes, metabolic functions, and cellular component localization were generated for the top 100 regulated genes using the aforementioned process in DGE analysis. Charts comprised of the top 25 genes were provided for each pairwise comparison.

The top 100 genes for each pairwise comparison was obtained from the set of differentially expressed genes and categorized as upregulated or downregulated. Genes with the highest or lowest expression were correlated to copper stress and can be used to partially describe the genetic response to copper. Protein descriptions with the “predicted protein” label indicated no assignment of any closely related protein or relevant GO terms from the UniProt database. Gene ontology terms and functional categorizations were assigned by the Omics Box/BLAST2GO program.

Results

Transcript assembly and QC analysis of sequences

The FastQC program was used to analyze the raw reads generated from Illumina sequencing. No sequences were flagged as poor quality. Copper resistant plants had 31–49 million sequences and copper susceptible plants had 21–29 million sequences. Both treatment groups had an average sequence length of 51 bases. The trinity program facilitated transcript assembly, producing 581,037 transcripts. Overall, 78–83% of genes were mapped to the database for copper resistant individuals, and 62% for copper susceptible genotypes. A total of 126,460 genes fulfilled the CPM related parameters and were used for differential gene expression analysis.

Differential gene expression (DGE) analysis between genotypes

This transcriptome shotgun assembly project has been deposited in the NCBI BioProject database with the accession number PRJNA962116. The clustering among samples was visually assessed using a multidimensional scale plot and hierarchical cluster map. The water and potassium control groups clustered within the same region, indicating no significant difference in gene expression between the treatment groups. The presence of the potassium control did not significantly affect the treatment regimen. Clustering between the resistant genotype (RG) and susceptible genotype (SG) was low, indicating that gene expression was significantly different between the two groups. In fact, 6,213 genes were upregulated and 29,038 genes were downregulated when RG were compared to SG (Table 1). For RG and the water control, clustering occurred within the same region and overlapped, demonstrating a similar pattern of gene expression. Only one gene was upregulated when RG wee compared to water control. No clustering was observed between SG and the water control. DEGs that fulfilled the high stringency cut off (two fold and FDR 0.05) were considered for downstream DGE analysis. The heatmaps and the volcano plots of the differentially expressed genes for copper RG compared to copper SG, RG compared to water, and SG compared to water are illustrated in Figs 1 and 2.

thumbnail
Fig 1.

Heatmap of differentially expressed genes in Pinus banksiana a) Copper resistant genotype compared to copper susceptible genotype; b) Copper resistant genotype compared to water control; and c) Copper susceptible genotype compared to water control. Differentially expressed gene values are based on the Log2 normalized FC, with red cells representing upregulation and blue cells representing downregulation. Cus542, Cus16 and Cus42 are copper susceptible samples. Cur872, Cur33 and Cur67 are copper resistant samples. Cuw37, CuW14 and Niw73 are the water controls.

https://doi.org/10.1371/journal.pone.0296027.g001

thumbnail
Fig 2.

Volcano plot of differentially expressed genes from Pinus banksiana: a) Copper resistant genotype compared to copper susceptible genotype; b) Copper resistant genotype compared to water controls; and c) Copper susceptible genotype compared to water controls. Brown points represent upregulated gene expression whereas blue points represent downregulated gene expression when compared to the susceptible genotype. Grey points indicate no significant difference from the susceptible genotypes. Log10(FDR) is the log10 of the false discovery rate. The border between the no significant points and the differentially regulated genes represents the false discovery rate of 0.05 (two fold).

https://doi.org/10.1371/journal.pone.0296027.g002

thumbnail
Table 1. Differentially expressed genes from the copper resistant genotype compared to the copper susceptible and water and copper susceptible genotypes compared to water in Pinus banksiana.

https://doi.org/10.1371/journal.pone.0296027.t001

Gene ontology of the top 100 differentially expressed genes for Pinus banksiana

Overall, 581,037 transcripts were mapped to protein sequences in the UniProt database and the closest matches were used to annotate genes. Overall, 25,552 transcripts were assigned gene ontology. Tables 2 to 3 show the top 25 upregulated and downregulated genes when copper RG were compared to SG and Tables 4 and 5 when SG were compared to water. Extended data including the top 50 upregulated and downregulated genes when RG and SG, and SG and controls were compared and are described in Tables 2S to 5S in S1 File. More importantly, Table 6 described the two candidate genes associated with copper resistance in P. banksiana.

thumbnail
Table 2. Top 25 upregulated genes from copper resistant samples compared to copper susceptible samples in Pinus banksiana.

https://doi.org/10.1371/journal.pone.0296027.t002

thumbnail
Table 3. Top 25 downregulated genes from copper resistant samples compared to copper susceptible samples in Pinus banksiana.

https://doi.org/10.1371/journal.pone.0296027.t003

thumbnail
Table 4. Top 25 upregulated genes from copper susceptible samples compared to water controls in Pinus banksiana.

https://doi.org/10.1371/journal.pone.0296027.t004

thumbnail
Table 5. Top 25 downregulated genes from copper susceptible samples compared to water controls in Pinus banksiana.

https://doi.org/10.1371/journal.pone.0296027.t005

thumbnail
Table 6. Identified candidate genes from the top upregulated genes in copper resistant vs copper susceptible Pinus banksiana.

https://doi.org/10.1371/journal.pone.0296027.t006

Biological processes

Upregulated genes.

Fig 3 shows the top upregulated genes of RG compared to SG and susceptible compared to water distributed into different terms within the Biological processes category. For this category, the top upregulated genes revealed that the response to stress term (16.67%) comprised the largest proportion of gene expression followed by the biosynthetic process (12.5%), response to chemical (12.5%), signal transduction (8.33%), post-embryonic development (8.33%) and the lipid metabolic process (8.33%) (Fig 3A). These terms represented 66.66% of the expressed genes. Response to stress, response to chemical, response to light stimulus and response to endogenous stimulus share the parent term response to stimulus.

thumbnail
Fig 3.

The top 100 most upregulated genes from a) resistant genotypes compared to the susceptible genotypes and b) susceptible genotypes compared to water controls. They were grouped by Gene Ontology terms within the Biological Processes category using Omicsbox/BLAST2GO. Terms with lower than 2% of total gene expression were combined together and assigned the label “other”.

https://doi.org/10.1371/journal.pone.0296027.g003

When SG were compared to the water controls for the biological processes category, 63.63% of upregulated genes were distributed to the following subcategories: response to stress (24.24%), carbohydrate metabolic process (12.12%), response to biotic stimulus (9.09%), response to chemical (9.09%), and response to endogenous stimulus (9.09%) (Fig 3B). Five of the top 10 categories fall under the parent term response to stimulus.

Downregulated genes

When RG were compared to the SG, for the biological processes category, 22.22% of genes were distributed to the carbohydrate metabolic process term (Fig 4A). Genes coding for signal transduction, response to stress, cellular component organisation, response to chemical, response to external stimulus, fruit ripening, and response to endogenous stimulus represented each 11,11% of the top downregulated genes (Fig 4A). Response to stress, response to chemicals, response to external stimulus, and response to endogenous stimulus share the parent term response to stimuli.

thumbnail
Fig 4.

Percentage of the top 100 downregulated transcripts in Pinus banksiana from a) resistant compared to the susceptible genotypes and b) susceptible genotypes compared to water controls. They were grouped by Gene Ontology terms within the Biological Processes category using Omicsbox/BLAST2GO. Terms with lower than 2% of total gene expression were combined together and assigned the label “other”.

https://doi.org/10.1371/journal.pone.0296027.g004

When SG were compared to the water control, for the Biological processes category, 52.17% of the downregulated genes were allocated to biosynthetic process (17.39%), response to stress (13.04%), lipid metabolic process (13.04%), and response to biotic stimulus (8.70%) (Fig 4B).

Metabolic function

Upregulated genes.

When RG were compared to SG, analysis of top upregulated genes revealed that 50% of expressed genes were associated with nucleotide binding followed by transporter activity (25%) and kinase activity (25%) (Fig 5A). This pattern changes when SG were compared to water with 61.54% of the top upregulated genes distributed to the hydrolase activity (38.46%) and transferase activity (23.08%) (Fig 5B). Hydrolase activity and transferase activity are categories that fall under the parent category catalytic activity whereas nucleotide binding and DNA binding categories are associated with nucleotide function.

thumbnail
Fig 5.

Percentage of the top 100 Upregulated transcripts in Pinus banksiana a) resistant genotypes compared to susceptible genotypes and b) susceptible samples compared to water categorized by Molecular Function. They were grouped by Gene Ontology terms within the Molecular Function category using Omicsbox/BLAST2GO. Terms with lower than 2% of total gene expression were combined together and assigned the label “other”.

https://doi.org/10.1371/journal.pone.0296027.g005

Downregulated genes.

Analysis of downregulated genes revealed that for the metabolic process category, 66.67% of expressed genes were allocated to the terms hydrolase activity (33.33%), DNA-binding transcription factor activity (16.67%), and transferase activity (16.67%) when RG and SG were compared (Fig 6A).

thumbnail
Fig 6.

Percentage of the top 100-downregulated transcripts in Pinus banksiana a) resistant genotypes compared to susceptible genotypes and b) susceptible samples compared to water categorized by Molecular Function. They were grouped by Gene Ontology terms within the Molecular Function category using Omicsbox/BLAST2GO. Terms with lower than 2% of total gene expression were combined together and assigned the label “other”.

https://doi.org/10.1371/journal.pone.0296027.g006

A different pattern of downregulated genes was observed when SG were compared to the water control. In fact, 69.23% of the expressed genes were categorized under hydrolase activity (46.15%) and transporter activity (23.08%) (Fig 6B).

Cellular compartment

Upregulated genes.

When RG were compared to SG, for the cellular component category, the membrane term comprised the largest portion of the top upregulated genes (60%) (S1a Fig in S2 File). The thylakoid organelle is also represented in the top upregulated genes. However, 66.67% of upregulated genes were distributed to the extracellular region (41.67%) and nucleus (25%) when SG were compared to water (S1b Fig in S2 File).

Downregulated genes.

The pattern of downregulated genes showed that for the cellular component category, 50% of expressed genes was associated with the extracellular region followed by the terms membrane (25%) and nucleus (25%) (S2a Fig in S2 File) when RG and SG were compared. Comparison of SG and water revealed that extracellular region (42.11%) and plasma membrane (21.05%) had the highest proportion of the top downregulated genes (S2b Fig in S2 File).

Discussion

DGE analysis of copper genotypes

A transcriptome analysis of Pinus banksiana treated with excess copper was performed to evaluate differences in global gene expression between different genotypes. Analyzing the transcriptome of resistant and susceptible seedlings can provide valuable insight on the molecular mechanisms associated with copper resistance or susceptibility in Pinus banksiana. The high number of DEGs in RG compared to SG at high stringency indicated that copper resistant plants had a significantly different pattern of gene expression compared to copper susceptible plants. Notably, the large proportion of downregulated genes compared to upregulated genes suggests a decline in many cellular processes. In RG compared to water, the very low number of DEGs at a high stringency indicates a similar pattern of gene expression between resistant plants and untreated plants. Several studies have demonstrated the significance of a single transporter or chelator gene on copper resistance and overall growth outcomes [17, 20, 33]. The large deviation in gene expression for SG compared to both RG and the water group suggests that there may be genetic and molecular factors contributing to copper susceptibility. The number of DEGs was also considerably higher in SG compared to water, implying that copper susceptibility was characterized by a large deviation from untreated conditions. This raises the possibility that DEGs in SG were also associated with death coping mechanisms responding to copper induced stress and tissue damage. This pattern of gene expression was also observed in Populus tremuloides when exposed to excess nickel [34].

Identification of candidate genes associated with copper resistance in Pinus banksiana

Analysis of the top upregulated genes revealed two promising candidate genes that may be involved in copper resistance mechanisms for Pinus banksiana. A candidate gene encoding a heavy metal-associated isoprenylated plant (HIPP) protein was identified. HIPP proteins are metallochaperones that chelate and deliver heavy metal ions to various proteins across cellular compartments [35]. The conserved protein structure of HIPP family proteins is comprised of a cysteine rich heavy metal associated (HMA) domain facilitating the binding of heavy metals and an isoprenylaton site involved in cellular compartment localization and signal transduction [3537]. Structural variation within the isoprenylated site offers the functional diversity needed to facilitate cellular compartment localization and protein targeting [37, 38]. In yeast, the overexpression of HIPP conferred resistance to copper, cadmium, and zinc [39]. Additionally, overexpression of HIPP in Arabidopsis thaliana conferred cadmium resistance [40]. Studies that demonstrated the binding of HIPP to copper, cadmium and zinc in plants corroborates the function of HIPP in the detoxification of heavy metals [38, 41]. The capture of copper ions by cysteine rich chelators is an essential mechanism that prevents excess copper from inhibiting enzymes, causing protein misfolding and generating ROS [42]. Although the specific protein targeted by AtHIPP20 are currently unknown, possible targets of metallochaperone mediated ion delivery include transporters, enzymes or other chaperones [39].

Another identified candidate gene encodes the Pleiotropic drug resistance (PDR) protein, which is an ATP-binding cassette (ABC) transporter [43]. ABC transporters are membrane localized transporters that facilitate the movement of a large diversity of entities via an ATP hydrolysis motif [44, 45]. The conserved protein region of ABC transporters include two nucleotide binding folds associated with ATP hydrolysis and two hydrophobic membrane domains involved in the determination of substrate specificity [44, 46]. The broad substrate specificity of PDR proteins often includes heavy metals, resulting in its involvement in heavy metal homeostasis as it pertains to the cytosol and the region external to the membrane [47]. In addition to heavy metal, PDR is also able to transport phytohormones, antifungal agents, and metabolites with antimicrobial properties [4850]. In Arabidopsis thaliana, an overexpression of AtPDR8 conferred cadmium resistance and reduced total cadmium content by exporting cadmium from the cytosol to the apoplast [47]. Similarly, upregulated AtPDR12 expression increased lead export from the cytosol which subsequently decreased lead content and contributed to lead resistance [51]. A possible role of PDR in copper detoxification may involve utilizing a similar efflux mechanism to export copper away from the cytosol and plasma membrane. The suppression of PDR in certain species treated with cadmium or lead resulted in severe growth defects, establishing PDR as a crucial component in heavy metal detoxification [51, 52]. Hormones such as Jasmonic acid and ABA induced the upregulation of Ospdr9, suggesting that PDR may also play a secondary role in mediating the general stress response [49, 53]. Further research is needed to describe how PDR contributes to copper detoxification in Pinus banksiana.

It should be pointed out that the two putative copper resistance genes encoding for HIPP and PDR proteins were not identified in SG and water-treated genotypes. It is likely that these genes are involved in copper resistance in P. banksiana since all the tissues collected from the SG were healthy. The effects of observed damages to SG on gene expression in healthy parts of the plants are unknown and cannot be completely discarded. A recent study shows that HIPP gene family plays a crucial role in cadmium resistance and accumulation in woody plant species such as the tea plant (Camellia sinensis L.) [54]. This study opens the door to further investigations to validate the role of HIPP and PDR in P. banksiana resistance to copper.

GO annotation of the top 25 upregulated genes between the resistant genotype and the susceptible genotype

Many of the top upregulated genes in RG compared to SG were involved in the stress response and may contribute to copper tolerance. The gene encoding terpene synthase (TPS) was among the top upregulated genes. TPS synthesizes 1,8-cineole and other terpenoids that partake in a variety of defense functions such as thermoregulation, resin assisted wound sealing, and plant to plant signalling [5557]. In response to heavy metals, terpenoids may scavenge ROS, mainly exerting its protective effect on membranes [58]. Terpenoids can also enhance the stability and rigidity of the chloroplast membrane by increasing the hydrophobic bonding between lipids [59, 60]. Enhancing the stability of membranes is a protective mechanism for resisting ROS mediated damage and lipid peroxidation caused by copper toxicity [61, 62].

A gene encoding a Fatty acyl-CoA reductase (FAR) was also identified among the top upregulated genes. FAR catalyzes the synthesis of fatty alcohols from fatty acyl-coA and serves an integral part in the acyl-reduction pathway [63]. Fatty alcohols are used as components for larger extracellular lipid compounds such as cuticular wax and suberin in response to heavy metals [64, 65]. These compounds (cuticular wax and suberin) form a hydrophobic barrier that blocks and protects cells against copper induced water loss when secreted onto the surface of leaves [66, 67]. The negative regulation of water transpiration is crucial to counteract water loss and drought which could induce further tissue damage [67].

Genes encoding Early light-induced proteins (ELIP) were also identified. ELIPs are photoactive proteins that regulate chloroplast content, counteract the photoinhibition of photosystem II, and safeguards photosynthesis machinery [68, 69]. Copper stress decreases chloroplast concentration, diminishes thylakoid membranes and replaces the iron cofactor in plastoquinone QA of photosystem II [9]. Notably, the inhibition of plastoquinone QA results in a reduction of electron transfer and subsequent light absorption [8, 9]. The collective effect of copper on chloroplast function may result in photodamage and ROS mediated damage [70, 71]. Upregulation of ELIP may potentially serve a photoprotective role to preserve chloroplast function and light absorption, although the exact mechanism of action has yet to be described [69].

GO annotation of the top 25 downregulated genes between the resistant genotype and the susceptible genotype

Several top downregulated genes encode enzymes involved in carbohydrate metabolism. An identified gene encodes polygalactuornase (pectinase), which facilitates the hydrolysis of the alpha-1,4 glycosidic bonds present in polygalacturnoan (pectin) [72]. Pectin is an essential component of the cell wall and is responsible for cell to cell adhesion [73]. Pectinase downregulation could potentially contribute to copper tolerance by preserving pectin content, thereby maintaining the integrity of the cell wall. It has been reported that downregulation of pectinase improved tolerance to multiple stressors by decreasing cell expansion, cell separation and increasing cell density [72, 74, 75]. Several genes that encode for beta glucosidase which is an enzyme that facilitates the conversion of cellobiose to glucose have been identified [76]. Beta glucosidase is an integral component of cellulose breakdown and was found to be expressed in the cell wall of some plants [77, 78]. Cellulose is the most abundant component of the cell wall, cellulose and it provides the tensile and turgor pressure required to maintain structural integrity [79, 80]. Downregulation of beta glucosidase upregulates cellulose production and also contributes to the maintenance of the cell wall in response to various stressors [81, 82]. The cell wall plays a crucial role in copper detoxification by acting as a site of sequestration and heavy metal distribution [83, 84]. The role of pectinase and beta glucosidase in maintaining the integrity of the cell wall is supported by the upregulation of the PDR transporter candidate gene, which has been previously shown to transport cadmium from the cytosol to the apoplast [47].

A gene encoding a trypsin inhibitor was identified in the top downregulated genes. Trypsin inhibitors mitigate the activity of serine proteases and prevent the breakdown of associated proteins [85]. Protein damage and misfolding caused by heavy metal binding and ROS interaction induces the production of serine proteases [86, 87]. Downregulation of trypsin inhibitors suggests that higher levels of serine protease activity were needed to breakdown damage or misfolded proteins thereby improving cell viability. Other studies reported variation in trypsin inhibitor activity in response to excess copper, suggesting that the activity is dependent on the extent of protein damage [88, 89].

GO annotation of the top 25 upregulated genes between the susceptible genotype and the control

In addition to stress related mechanisms triggered by excess copper, the examination of upregulated genes observed when SG and water were compared could reveal genes associated with copper susceptibility or plant cell death and necrosis. Genes encoding the trypsin inhibitor, were among the top upregulated genes. They were previously found to be downregulated in RG when compared to SG. The upregulation of trypsin inhibitors in SG may indicate a larger amount of serine protease activity. Increased ROS production and undesired copper binding cause protein misfolding and damage which can elicit serine protease activity [86, 87]. Overexpression of serine protease may damage plant tissue and cause a further reduction in protein content [90]. The upregulation of trypsin inhibitors could therefore be a protective strategy to conserve protein content and delay senescence [91, 92]. Upregulation of trypsin inhibitors in other plants has also been reported in response to other stressors such as drought and fungal infection [93, 94].

In contrast to gene expression observed when RG compared to SG, many of the top upregulated genes encoded beta glucosidase. The upregulation of beta glucosidase increases the conversion of cellobiose and other sugars to glucose, implying a metabolic related function. An adverse side effect of upregulated beta glucosidase is a decrease in cellulose content which may compromise the strength and integrity of the cell wall [95]. Some studies demonstrated that beta glucosidase may play a possible role in the stress response by regulating ABA levels [9698]. Other studies reported a correlation between beta glucosidase overexpression and the production of antioxidant flavonols which may also contribute to stress alleviation [99].

GO annotation of the top 25 downregulated genes between the susceptible genotype and the control

Among the top downregulated genes in SG compared to the control were genes encoding the probable aquaporin proteins PIP2-8. Aquaporins are membrane bound channels that serve as an important point of entry for water, nutrients, and heavy metals [100]. The broad specificity of Aquaporins provides a potential point of regulation to control the transport of heavy metals. Downregulation of aquaporins could also be a response to increased transpiration and water loss caused by heavy metals [101].

A gene encoding the WALLS ARE THIN1 (WAT1) protein was also identified among the top downregulated genes. WAT1 is an auxin transporter that is localized to the vacuole, facilitating the movement of auxin to the cytoplasm [102]. Excess copper can deregulate auxin homeostasis and distribution which can negatively impact various aspects of plant development [103, 104]. In particular, the deregulation of auxin can affect cell division, cell elongation, leaf morphogenesis, and hormone crosstalk, [103, 105, 106]. In response to copper stress, the downregulation of WAT1 could be a strategy to safeguard growth by altering the transport and intracellular distribution of auxin. However, the response of WAT1 to copper specifically is not fully understood. Downregulation of WAT1 may also regulate salicylic acid synthesis which coordinates the stress response [107, 108].

Conclusion

A comprehensive transcriptome analysis was conducted on copper treated Pinus banksiana to understand the genetic response of different genotypes to copper. There were 19,789 DEGs between RG and SG at a high stringency, indicating significant differences in gene expression between resistant and susceptible plants. The low number of DEGs when RG were compared to water control indicated a similar pattern of gene expression. SG had a large number of DEGs compared to both RG and the control, suggesting that SG had a different set of coping mechanisms from the aforementioned groups. It is also possible that genes associated with plant death might interfere with the expression of some genes even if the tissues analyzed were undamaged.

Gene Ontology of the top upregulated genes in RG compared to SG showed that the response to stress had the highest proportion of expressed genes. The carbohydrate metabolic process term had the highest percentage of downregulated genes. AtHIPP20 and AtHIPP26 encoding a metallochaperone along with NtPDR1 encoding an ATP binding cassette transporter, were candidate genes associated with copper resistance in P. banksiana. Other identified top upregulated genes were associated with the coordination of the stress response and included TPS, AtFAR2 and ELIP1. Top downregulated genes included polygalacturonase and beta glucosidase that may play a role in the strengthening of the cell wall and the sequestration of copper ions. This study demonstrated the strong utility of transcriptome analysis for elucidating the genetic response of plants and associated genotypes to copper stress. The identified candidate genes should be further researched to evaluate potential applications in various industries.

Acknowledgments

We would like to thank the Natural Sciences and Engineering Research Council of Canada (NSERC) for financial support and Seq Matic (Fremont California) for RNA sequencing.

References

  1. 1. Ghuge S, Tisi A, Carucci A, Rodrigues-Pousada R, Franchi S, Tavladoraki P, et al. Cell Wall Amine Oxidases: New Players in Root Xylem Differentiation under Stress Conditions. Plants. 2015;4: 489–504. pmid:27135338
  2. 2. Shahbaz M, Ravet K, Peers G, Pilon M. Prioritization of copper for the use in photosynthetic electron transport in developing leaves of hybrid poplar. Front Plant Sci. 2015;6. pmid:26089828
  3. 3. Garcia-Molina A, Andrés-Colás N, Perea-García A, del Valle-Tascón S, Peñarrubia L, Puig S. The intracellular Arabidopsis COPT5 transport protein is required for photosynthetic electron transport under severe copper deficiency. Plant J. 2011;65: 848–860. pmid:21281364
  4. 4. Chamseddine M, Wided BA, Guy H, Marie-Edith C, Fatma J. Cadmium and copper induction of oxidative stress and antioxidative response in tomato (Solanum lycopersicon) leaves. Plant Growth Regul. 2008;57: 89–99.
  5. 5. Lin S-L, Wu L. Effects of copper concentration on mineral nutrient uptake and copper accumulation in protein of copper-tolerant and nontolerant Lotus purshianus L. Ecotoxicol Environ Saf. 1994;29: 214–228. pmid:7533712
  6. 6. Ivanov YV, Kartashov AV, Ivanova AI, Savochkin YV, Kuznetsov VV. Effects of copper deficiency and copper toxicity on organogenesis and some physiological and biochemical responses of Scots pine (Pinus sylvestris L.) seedlings grown in hydroculture. Environ Sci Pollut Res. 2016;23: 17332–17344. pmid:27225009
  7. 7. Martins LL, Mourato MP. Effect of Excess Copper on Tomato Plants: Growth Parameters, Enzyme Activities, Chlorophyll, and Mineral Content. J Plant Nutr. 2006;29: 2179–2198.
  8. 8. Jegerschoeld C, Arellano JB, Schroeder WP, van Kan PJM, Baron M, Styring S. Copper(II) Inhibition of Electron Transfer through Photosystem II Studied by EPR Spectroscopy. Biochemistry. 1995;34: 12747–12754. pmid:7548028
  9. 9. Pätsikkä E, Kairavuo M, Šeršen F, Aro E-M, Tyystjärvi E. Excess Copper Predisposes Photosystem II to Photoinhibition in Vivo by Outcompeting Iron and Causing Decrease in Leaf Chlorophyll. Plant Physiol. 2002;129: 1359–1367. pmid:12114589
  10. 10. Opdenakker K, Remans T, Keunen E, Vangronsveld J, Cuypers A. Exposure of Arabidopsis thaliana to Cd or Cu excess leads to oxidative stress mediated alterations in MAPKinase transcript levels. Environ Exp Bot. 2012;83: 53–61.
  11. 11. Wang X, Zhi J, Liu X, Zhang H, Liu H, Xu J. Transgenic tobacco plants expressing a P1B-ATPase gene from Populus tomentosa Carr. (PtoHMA5) demonstrate improved cadmium transport. Int J Biol Macromol. 2018;113: 655–661. pmid:29501753
  12. 12. Sharma R, Bhardwaj R, Thukral AK, Al-Huqail AA, Siddiqui MH, Ahmad P. Oxidative stress mitigation and initiation of antioxidant and osmoprotectant responses mediated by ascorbic acid in Brassica juncea L. subjected to copper (II) stress. Ecotoxicol Environ Saf. 2019;182: 109436. pmid:31325808
  13. 13. Nair PM, Gopalakrishnan , Chung IM. Impact of copper oxide nanoparticles exposure on Arabidopsis thaliana growth, root system development, root lignificaion, and molecular level changes. Environ Sci Pollut Res Int. 2014;21: 12709–22. pmid:24965006
  14. 14. Sancenón V, Puig S, Mateu-Andrés I, Dorcey E, Thiele DJ, Peñarrubia L. The Arabidopsis Copper Transporter COPT1 Functions in Root Elongation and Pollen Development*. J Biol Chem. 2004;279: 15348–15355. pmid:14726516
  15. 15. del Pozo T, Cambiazo V, González M. Gene expression profiling analysis of copper homeostasis in Arabidopsis thaliana. Biochem Biophys Res Commun. 2010;393: 248–252. pmid:20117084
  16. 16. Wintz H, Fox T, Wu Y-Y, Feng V, Chen W, Chang H-S, et al. Expression Profiles of Arabidopsis thaliana in Mineral Deficiencies Reveal Novel Transporters Involved in Metal Homeostasis. J Biol Chem. 2003;278: 47644–47653. pmid:13129917
  17. 17. Andrés-Colás N, Sancenón V, Rodríguez-Navarro S, Mayo S, Thiele DJ, Ecker JR, et al. The Arabidopsis heavy metal P-type ATPase HMA5 interacts with metallochaperones and functions in copper detoxification of roots. Plant J. 2006;45: 225–236. pmid:16367966
  18. 18. Deng F, Yamaji N, Xia J, Ma JF. A Member of the Heavy Metal P-Type ATPase OsHMA5 Is Involved in Xylem Loading of Copper in Rice. Plant Physiol. 2013;163: 1353–1362. pmid:24064929
  19. 19. Boutigny S, Sautron E, Finazzi G, Rivasseau C, Frelet-Barrand A, Pilon M, et al. HMA1 and PAA1, two chloroplast-envelope PIB-ATPases, play distinct roles in chloroplast copper homeostasis. J Exp Bot. 2014;65: 1529–1540. pmid:24510941
  20. 20. Lee S, Kim Y-Y, Lee Y, An G. Rice P1B-Type Heavy-Metal ATPase, OsHMA9, Is a Metal Efflux Protein. Plant Physiol. 2007;145: 831–842. pmid:17827266
  21. 21. Mayerhofer H, Sautron E, Rolland N, Catty P, Seigneurin-Berny D, Pebay-Peyroula E, et al. Structural Insights into the Nucleotide-Binding Domains of the P1B-type ATPases HMA6 and HMA8 from Arabidopsis thaliana. Dmitriev OY, editor. PLOS ONE. 2016;11: e0165666. pmid:27802305
  22. 22. Tapken W, Ravet K, Pilon M. Plastocyanin Controls the Stabilization of the Thylakoid Cu-transporting P-type ATPase PAA2/HMA8 in Response to Low Copper in Arabidopsis. J Biol Chem. 2012;287: 18544–18550. pmid:22493454
  23. 23. Tapken W, Ravet K, Shahbaz M, Pilon M. Regulation of Cu delivery to chloroplast proteins. Plant Signal Behav. 2015;10: e1046666. pmid:26251885
  24. 24. Zhang B, Shang S, Jabeen Z, Zhang G. Involvement of ethylene in alleviation of Cd toxicity by NaCl in tobacco plants. Ecotoxicol Environ Saf. 2014;101: 64–69. pmid:24507128
  25. 25. Zhou J, Goldsbrough PB. Structure, organization and expression of the metallothionein gene family inArabidopsis. Mol Gen Genet MGG. 1995;248: 318–328. pmid:7565594
  26. 26. Guo W-J, Bundithya W, Goldsbrough PB. Characterization of the Arabidopsis Metallothionein Gene Family: Tissue-Specific Expression and Induction during Senescence and in Response to Copper. New Phytol. 2003;159: 369–381. pmid:33873353
  27. 27. Beckett P, Spiers G. Sudbury, Canada -40 years of a Community Regreening on a Smelter-Impacted Landscape Before After. Available: https://www.atlanticclra.ca/wp-content/uploads/2018/11/Beckett-Presentation.pdf
  28. 28. Lu P, Parker WH, Cherry M, Colombo S, Parker WC, Man R, et al. Survival and growth patterns of white spruce (Picea glauca [M oench] Voss) rangewide provenances and their implications for climate change adaptation. Ecol Evol. 2014;4: 2360–2374. pmid:25360273
  29. 29. Nkongolo KK, Spiers G, Beckett P, Narendrula R, Theriault G, Tran A, et al. Long-Term Effects of Liming on Soil Chemistry in Stable and Eroded Upland Areas in a Mining Region. Water Air Soil Pollut. 2013;224: 1618.
  30. 30. Vandeligt KK, Nkongolo KK, Mehes M, Beckett P. Genetic analysis of Pinus banksiana and Pinus resinosa populations from stressed sites contaminated with metals in Northern Ontario (Canada). Chem Ecol. 2011;27: 369–380.
  31. 31. Ranger M, Nkongolo KK, Michael P, Beckett P. Genetic Differentiation of Jack Pine (Pinus banksiana) and Red Pine (P. resinosa) Populations From Metal Contaminated Areas in Northern Ontario (Canada) Using ISSR Markers. Silvae Genet. 2008;57: 333–340.
  32. 32. Moarefi N, Nkongolo KK. Contrasting tolerance and gene expression between white pine (Pinus strobus) and jack pine (P. banksiana) exposed to an increasing nickel concentration. Ecol Genet Genomics. 2022;24: 100124.
  33. 33. Guo W-J, Meetam M, Goldsbrough PB. Examining the Specific Contributions of Individual Arabidopsis Metallothioneins to Copper Distribution and Metal Tolerance. Plant Physiol. 2008;146: 1697–1706. pmid:18287486
  34. 34. Czajka KM, Nkongolo K. Transcriptome analysis of trembling aspen (Populus tremuloides) under nickel stress. PLoS ONE. 2022;17: e0274740. pmid:36227867
  35. 35. de Abreu-Neto JB, Turchetto-Zolet AC, de Oliveira LFV, Bodanese Zanettini MH, Margis-Pinheiro M. Heavy metal-associated isoprenylated plant protein (HIPP): characterization of a family of proteins exclusive to plants. FEBS J. 2013;280: 1604–1616. pmid:23368984
  36. 36. Tehseen M, Cairns N, Sherson S, Cobbett CS. Metallochaperone-like genes in Arabidopsis thaliana†. Metallomics. 2010;2: 556–564. pmid:21072340
  37. 37. Barth O, Vogt S, Uhlemann R, Zschiesche W, Humbeck K. Stress induced and nuclear localized HIPP26 from Arabidopsis thaliana interacts via its heavy metal associated domain with the drought stress related zinc finger transcription factor ATHB29. Plant Mol Biol. 2009;69: 213–226. pmid:18974936
  38. 38. Gao W, Xiao S, Li H-Y, Tsao S-W, Chye M-L. Arabidopsis thaliana acyl-CoA-binding protein ACBP2 interacts with heavy-metal-binding farnesylated protein AtFP6. New Phytol. 2009;181: 89–102. pmid:18823312
  39. 39. khan I ullah Rono JK, Zhang BQ Liu XS, Wang MQ Wang LL, et al. Identification of novel rice (Oryza sativa) HPP and HIPP genes tolerant to heavy metal toxicity. Ecotoxicol Environ Saf. 2019;175: 8–18. pmid:30878662
  40. 40. Suzuki N, Yamaguchi Y, Koizumi N, Sano H. Functional characterization of a heavy metal binding protein CdI19 from Arabidopsis. Plant J. 2002;32: 165–173. pmid:12383082
  41. 41. Dykema PE, Sipes PR, Marie A, Biermann BJ, Crowell DN, Randall SK. A new class of proteins capable of binding transition metals. Plant Mol Biol. 1999;41: 139–150. pmid:10561075
  42. 42. Zhang X, Feng H, Feng C, Xu H, Huang X, Wang Q, et al. Isolation and characterisation of cDNA encoding a wheat heavy metal-associated isoprenylated protein involved in stress responses. Plant Biol. 2015;17: 1176–1186. pmid:25951496
  43. 43. Crouzet J, Roland J, Peeters E, Trombik T, Ducos E, Nader J, et al. NtPDR1, a plasma membrane ABC transporter from Nicotiana tabacum, is involved in diterpene transport. Plant Mol Biol. 2013;82: 181–192. pmid:23564360
  44. 44. Fernandez LR, Vandenbussche G, Roosens N, Govaerts C, Goormaghtigh E, Verbruggen N. Metal binding properties and structure of a type III metallothionein from the metal hyperaccumulator plant Noccaea caerulescens. Biochim Biophys Acta BBA—Proteins Proteomics. 2012;1824: 1016–1023. pmid:22668884
  45. 45. Ogasawara F, Kodan A, Ueda K. ABC proteins in evolution. FEBS Lett. 2020;594: 3876–3881. pmid:33002191
  46. 46. Moody JE, Millen L, Binns D, Hunt JF, Thomas PJ. Cooperative, ATP-dependent Association of the Nucleotide Binding Cassettes during the Catalytic Cycle of ATP-binding Cassette Transporters *. J Biol Chem. 2002;277: 21111–21114. pmid:11964392
  47. 47. Kim D-Y, Bovet L, Maeshima M, Martinoia E, Lee Y. The ABC transporter AtPDR8 is a cadmium extrusion pump conferring heavy metal resistance. Plant J. 2007;50: 207–218. pmid:17355438
  48. 48. Kang J, Hwang J-U, Lee M, Kim Y-Y, Assmann SM, Martinoia E, et al. PDR-type ABC transporter mediates cellular uptake of the phytohormone abscisic acid. Proc Natl Acad Sci. 2010;107: 2355–2360. pmid:20133880
  49. 49. Zhang H, Jing W, Zheng J, Jin Y, Wu D, Cao C, et al. The ATP-binding cassette transporter OsPDR1 regulates plant growth and pathogen resistance by affecting jasmonates biosynthesis in rice. Plant Sci. 2020;298: 110582. pmid:32771142
  50. 50. Pierman B, Toussaint F, Bertin A, Lévy D, Smargiasso N, De Pauw E, et al. Activity of the purified plant ABC transporter NtPDR1 is stimulated by diterpenes and sesquiterpenes involved in constitutive and induced defenses. J Biol Chem. 2017;292: 19491–19502. pmid:28972149
  51. 51. Lee M, Lee K, Lee J, Noh EW, Lee Y. AtPDR12 Contributes to Lead Resistance in Arabidopsis. Plant Physiol. 2005;138: 827–836. pmid:15923333
  52. 52. Li He, Li Chao, Sun Di, Yang Zhimin. OsPDR20 is an ABCG metal transporter regulating cadmium accumulation in rice. J Environ Sci China. 2022; pmid:37923431
  53. 53. Moons A. Ospdr9, which encodes a PDR-type ABC transporter, is induced by heavy metals, hypoxic stress and redox perturbations in rice roots 1. FEBS Lett. 2003;553: 370–376. pmid:14572653
  54. 54. Wei Y, Peng X, Wang X, Wang C. The heavy metal-associated isoprenylated plant protein (HIPP) gene family plays a crucial role in cadmium resistance and accumulation in the tea plant (Camellia sinensis L.). Ecotoxicol Environ Saf. 2023;260: 115077. pmid:37257351
  55. 55. Keeling CI, Weisshaar S, Ralph SG, Jancsik S, Hamberger B, Dullat HK, et al. Transcriptome mining, functional characterization, and phylogeny of a large terpene synthase gene family in spruce (Picea spp.). BMC Plant Biol. 2011;11: 43. pmid:21385377
  56. 56. Kaitera J, Piispanen J, Bergmann U. Terpene and resin acid contents in Scots pine stem lesions colonized by the rust fungus Cronartium pini. For Pathol. 2021;51: e12700.
  57. 57. Sharma E, Anand G, Kapoor R. Terpenoids in plant and arbuscular mycorrhiza-reinforced defence against herbivorous insects. Ann Bot. 2017;119: 791–801. pmid:28087662
  58. 58. Loreto F, Mannozzi M, Maris C, Nascetti P, Ferranti F, Pasqualini S. Ozone Quenching Properties of Isoprene and Its Antioxidant Role in Leaves. Plant Physiol. 2001;126: 993–1000. pmid:11457950
  59. 59. Velikova V, Várkonyi Z, Szabó M, Maslenkova L, Nogues I, Kovács L, et al. Increased Thermostability of Thylakoid Membranes in Isoprene-Emitting Leaves Probed with Three Biophysical Techniques. Plant Physiol. 2011;157: 905–916. pmid:21807886
  60. 60. Siwko ME, Marrink SJ, de Vries AH, Kozubek A, Schoot Uiterkamp AJM, Mark AE. Does isoprene protect plant membranes from thermal shock? A molecular dynamics study. Biochim Biophys Acta BBA—Biomembr. 2007;1768: 198–206. pmid:17125733
  61. 61. Wang S, He T, Xu F, Li X, Yuan L, Wang Q, et al. Analysis of physiological and metabolite response of Celosia argentea to copper stress. Plant Biol. 2021;23: 391–399. pmid:32722892
  62. 62. Farghaly FA, Hamada AM, Radi AA. Phyto-remedial of excessive copper and evaluation of its impact on the metabolic activity of Zea mays. Cereal Res Commun. 2022;50: 973–985.
  63. 63. Kunst L, Samuels AL. Biosynthesis and secretion of plant cuticular wax. Prog Lipid Res. 2003;42: 51–80. pmid:12467640
  64. 64. Doan TTP, Domergue F, Fournier AE, Vishwanath SJ, Rowland O, Moreau P, et al. Biochemical characterization of a chloroplast localized fatty acid reductase from Arabidopsis thaliana. Biochim Biophys Acta BBA—Mol Cell Biol Lipids. 2012;1821: 1244–1255. pmid:22166367
  65. 65. Zhang X, Liu Y, Ayaz A, Zhao H, Lü S. The Plant Fatty Acyl Reductases. Int J Mol Sci. 2022;23: 16156. pmid:36555796
  66. 66. Wang Y, Sun Y, You Q, Luo W, Wang C, Zhao S, et al. Three Fatty Acyl-Coenzyme A Reductases, BdFAR1, BdFAR2 and BdFAR3, are Involved in Cuticular Wax Primary Alcohol Biosynthesis in Brachypodium distachyon. Plant Cell Physiol. 2018;59: 527–543. pmid:29329458
  67. 67. Mostofa MG, Fujita M. Salicylic acid alleviates copper toxicity in rice (Oryza sativa L.) seedlings by up-regulating antioxidative and glyoxalase systems. Ecotoxicology. 2013;22: 959–973. pmid:23579392
  68. 68. Liu X, Zhang Y, Yang H, Liang Y, Li X, Oliver MJ, et al. Functional Aspects of Early Light-Induced Protein (ELIP) Genes from the Desiccation-Tolerant Moss Syntrichia caninervis. Int J Mol Sci. 2020;21: 1411. pmid:32093042
  69. 69. Tao L, Zeba N, Ashrafuzzaman M, Hong CB. Heavy metal stress-inducible early light-inducible gene CaELIP from hot pepper (Capsicum annuum) shows broad expression patterns under various abiotic stresses and circadian rhythmicity. Environ Exp Bot. 2011;72: 297–303.
  70. 70. Caspi V, Droppa M, Horváth G, Malkin S, Marder JB, Raskin VI. The effect of copper on chlorophyll organization during greening of barley leaves. Photosynth Res. 1999;62: 165–174.
  71. 71. Lindahl M, Funk C, Webster J, Bingsmark S, Adamska I, Andersson B. Expression of ELIPs and PS II-S protein in spinach during acclimative reduction of the Photosystem II antenna in response to increased light intensities. Photosynth Res. 1997;54: 227–236.
  72. 72. Atkinson RG, Sutherland PW, Johnston SL, Gunaseelan K, Hallett IC, Mitra D, et al. Down-regulation of POLYGALACTURONASE1 alters firmness, tensile strength and water loss in apple (Malus x domestica) fruit. BMC Plant Biol. 2012;12: 129. pmid:22856470
  73. 73. Orfila C, Huisman MM, Willats WG, van Alebeek G-JW, Schols HA, Seymour GB, et al. Altered cell wall disassembly during ripening of Cnr tomato fruit: implications for cell adhesion and fruit softening. Planta. 2002;215: 440–447. pmid:12111226
  74. 74. Liu H, Ma Y, Chen N, Guo S, Liu H, Guo X, et al. Overexpression of stress-inducible OsBURP16, the β subunit of polygalacturonase 1, decreases pectin content and cell adhesion and increases abiotic stress sensitivity in rice. Plant Cell Environ. 2014;37: 1144–1158. pmid:24237159
  75. 75. Ohara T, Takeuchi H, Sato J, Nakamura A, Ichikawa H, Yokoyama R, et al. Structural Alteration of Rice Pectin Affects Cell Wall Mechanical Strength and Pathogenicity of the Rice Blast Fungus Under Weak Light Conditions. Plant Cell Physiol. 2021;62: 641–649. pmid:33543762
  76. 76. Chuenchor W, Pengthaisong S, Robinson RC, Yuvaniyama J, Oonanant W, Bevan DR, et al. Structural Insights into Rice BGlu1 β-Glucosidase Oligosaccharide Hydrolysis and Transglycosylation. J Mol Biol. 2008;377: 1200–1215. pmid:18308333
  77. 77. Nematollahi WP, Roux SJ. A Novel β-Glucosidase from the Cell Wall of Maize (Zea mays L.): Rapid Purification and Partial Characterization. J Plant Physiol. 1999;155: 462–469. pmid:11543181
  78. 78. Sasaki I, Nagayama H. Induction of β-Glucosidase in Botrytis cinerea by Cell Wall Fractions of the Host Plant. Biosci Biotechnol Biochem. 1997;61: 1073–1076.
  79. 79. McCann MC, Roberts K. Changes in cell wall architecture during cell elongation. J Exp Bot. 1994;45: 1683–1691.
  80. 80. Zhang Y, Yu J, Wang X, Durachko DM, Zhang S, Cosgrove DJ. Molecular insights into the complex mechanics of plant epidermal cell walls. Science. 2021;372: 706–711. pmid:33986175
  81. 81. Kalluri UC, Payyavula RS, Labbé JL, Engle N, Bali G, Jawdy SS, et al. Down-Regulation of KORRIGAN-Like Endo-β-1,4-Glucanase Genes Impacts Carbon Partitioning, Mycorrhizal Colonization and Biomass Production in Populus. Front Plant Sci. 2016;7. Available: https://www.frontiersin.org/articles/10.3389/fpls.2016.01455
  82. 82. Zheng M, Liu X, Lin J, Liu X, Wang Z, Xin M, et al. Histone acetyltransferase GCN5 contributes to cell wall integrity and salt stress tolerance by altering the expression of cellulose synthesis genes. Plant J. 2019;97: 587–602. pmid:30394596
  83. 83. Ren C, Qi Y, Huang G, Yao S, You J, Hu H. Contributions of root cell wall polysaccharides to Cu sequestration in castor (Ricinus communis L.) exposed to different Cu stresses. J Environ Sci. 2020;88: 209–216. pmid:31862062
  84. 84. Cao Y-Y, Qi C-D, Li S, Wang Z, Wang X, Wang J, et al. Melatonin Alleviates Copper Toxicity via Improving Copper Sequestration and ROS Scavenging in Cucumber. Plant Cell Physiol. 2019;60: 562–574. pmid:30496548
  85. 85. Hou W-C, Lin Y-H. Sweet potato (Ipomoea batatas (L.) Lam) trypsin inhibitors, the major root storage proteins, inhibit one endogenous serine protease activity. Plant Sci. 2002;163: 733–739.
  86. 86. Schützendübel A, Polle A. Plant responses to abiotic stresses: heavy metal‐induced oxidative stress and protection by mycorrhization. J Exp Bot. 2002;53: 1351–1365. pmid:11997381
  87. 87. Jacques S, Ghesquière B, De Bock P-J, Demol H, Wahni K, Willems P, et al. Protein Methionine Sulfoxide Dynamics in Arabidopsis thaliana under Oxidative Stress[S]. Mol Cell Proteomics. 2015;14: 1217–1229. pmid:25693801
  88. 88. Karmous I, Chaoui A, Jaouani K, Sheehan D, El Ferjani E, Scoccianti V, et al. Role of the ubiquitin-proteasome pathway and some peptidases during seed germination and copper stress in bean cotyledons. Plant Physiol Biochem. 2014;76: 77–85. pmid:24486582
  89. 89. Guerra FP, Reyes L, Vergara-Jaque A, Campos-Hernández C, Gutiérrez A, Pérez-Díaz J, et al. Populus deltoides Kunitz trypsin inhibitor 3 confers metal tolerance and binds copper, revealing a new defensive role against heavy metal stress. Environ Exp Bot. 2015;115: 28–37.
  90. 90. Jiang WB, Lers A, Lomaniec E, Aharoni N. Senescence-related serine protease in parsley. Phytochemistry. 1999;50: 377–382.
  91. 91. Radisky ES, Lee JM, Lu C-JK, Koshland DE. Insights into the serine protease mechanism from atomic resolution structures of trypsin reaction intermediates. Proc Natl Acad Sci. 2006;103: 6835–6840. pmid:16636277
  92. 92. Azeez A, Sane AP, Bhatnagar D, Nath P. Enhanced expression of serine proteases during floral senescence in Gladiolus. Phytochemistry. 2007;68: 1352–1357. pmid:17412375
  93. 93. Guretzki S, Papenbrock J. Characterization of Lablab purpureus Regarding Drought Tolerance, Trypsin Inhibitor Activity and Cyanogenic Potential for Selection in Breeding Programmes. J Agron Crop Sci. 2014;200: 24–35.
  94. 94. Tubajika KM, Damann KE. Sources of Resistance to Aflatoxin Production in Maize. J Agric Food Chem. 2001;49: 2652–2656. pmid:11368650
  95. 95. Jiang Y, Yin H, Wang D, Zhong Y, Deng Y. Exploring the mechanism of Akebia trifoliata fruit cracking based on cell-wall metabolism. Food Res Int. 2022;157: 111219. pmid:35761541
  96. 96. Lee KH, Piao HL, Kim H-Y, Choi SM, Jiang F, Hartung W, et al. Activation of Glucosidase via Stress-Induced Polymerization Rapidly Increases Active Pools of Abscisic Acid. Cell. 2006;126: 1109–1120. pmid:16990135
  97. 97. Liang B, Zheng Y, Wang J, Zhang W, Fu Y, Kai W, et al. Overexpression of the persimmon abscisic acid β-glucosidase gene (DkBG1) alters fruit ripening in transgenic tomato. Plant J. 2020;102: 1220–1233. pmid:31960511
  98. 98. Xu Z-Y, Lee KH, Dong T, Jeong JC, Jin JB, Kanno Y, et al. A Vacuolar β-Glucosidase Homolog That Possesses Glucose-Conjugated Abscisic Acid Hydrolyzing Activity Plays an Important Role in Osmotic Stress Responses in Arabidopsis. Plant Cell. 2012;24: 2184–2199. pmid:22582100
  99. 99. Baba SA, Vishwakarma RA, Ashraf N. Functional Characterization of CsBGlu12, a β-Glucosidase from Crocus sativus, Provides Insights into Its Role in Abiotic Stress through Accumulation of Antioxidant Flavonols. J Biol Chem. 2017;292: 4700–4713. pmid:28154174
  100. 100. Lopez-Zaplana A, Martinez-Garcia N, Carvajal M, Bárzana G. Relationships between aquaporins gene expression and nutrient concentrations in melon plants (Cucumis melo L.) during typical abiotic stresses. Environ Exp Bot. 2022;195: 104759.
  101. 101. Kholodova V, Volkov K, Abdeyeva A, Kuznetsov V. Water status in Mesembryanthemum crystallinum under heavy metal stress. Environ Exp Bot. 2011;71: 382–389.
  102. 102. Ranocha P, Dima O, Nagy R, Felten J, Corratgé-Faillie C, Novák O, et al. Arabidopsis WAT1 is a vacuolar auxin transport facilitator required for auxin homoeostasis. Nat Commun. 2013;4: 2625. pmid:24129639
  103. 103. Song Y, Zhou L, Yang S, Wang C, Zhang T, Wang J. Dose-dependent sensitivity of Arabidopsis thaliana seedling root to copper is regulated by auxin homeostasis. Environ Exp Bot. 2017;139: 23–30.
  104. 104. Yuan H-M, Xu H-H, Liu W-C, Lu Y-T. Copper Regulates Primary Root Elongation Through PIN1-Mediated Auxin Redistribution. Plant Cell Physiol. 2013;54: 766–778. pmid:23396597
  105. 105. Ku S-J, Park J-Y, Ha S-B, Kim J. Overexpression of IAA1 with domain II mutation impairs cell elongation and cell division in inflorescences and leaves of Arabidopsis. J Plant Physiol. 2009;166: 548–553. pmid:18771815
  106. 106. DEMASON DA, CHAWLA R. Auxin/gibberellin interactions in pea leaf morphogenesis. Bot J Linn Soc. 2006;150: 45–59.
  107. 107. Denancé N, Ranocha P, Oria N, Barlet X, Rivière M-P, Yadeta KA, et al. Arabidopsis wat1 (walls are thin1)-mediated resistance to the bacterial vascular pathogen, Ralstonia solanacearum, is accompanied by cross-regulation of salicylic acid and tryptophan metabolism. Plant J. 2013;73: 225–239. pmid:22978675
  108. 108. Wang D, Pajerowska-Mukhtar K, Culler AH, Dong X. Salicylic Acid Inhibits Pathogen Growth in Plants through Repression of the Auxin Signaling Pathway. Curr Biol. 2007;17: 1784–1790. pmid:17919906