Mol. Cells 2016; 39(2): 111-118
Published online December 15, 2015
https://doi.org/10.14348/molcells.2016.2188
© The Korean Society for Molecular and Cellular Biology
Correspondence to : *Correspondence: djyun@gnu.ac.kr (DJY); mckim@gnu.ac.kr (MCK)
Keywords ABA, abiotic stress, arabidopsis, drought, microRNA, salt
During growth and development, plants encounter a wide array of environmental stresses that trigger physiological and genetic responses (Chinnusamy and Zhu, 2009; Cushman and Bohnert, 2000). In addition, primary stresses lead to secondary stresses such as oxidative stress and thermal shock. Accordingly, plants have evolved various response mechanisms that help them adapt or acclimate to the stresses (Yamaguchi-Shinozaki and Shinozaki, 2006). A large proportion of plant genes are regulated by biotic (e.g., bacterial pathogens, virus, fungi, insects, and nematodes) (Brotman et al., 2012; Fagard et al., 2007) and abiotic stresses (e.g., drought, soil salinity, extreme temperatures, and heavy metals) (Chao et al., 2005; Si et al., 2009). Various cellular processes, such as RNA processing and post-transcriptional or even post-translational modifications, participate in regulation of the expression of genes in response to biotic and abiotic stresses.
MicroRNAs (miRNAs) can repress gene expression at the post-transcriptional level in plants (Bartel, 2004; Mallory and Vaucheret, 2006). MiRNAs are generally generated via a multistep process associated with the activation of
Recent studies have shown that plants respond to environmental stresses by modulating gene expression at post-transcriptional levels via miRNAs. MiRNAs act in a wide variety of metabolic and biological processes during plant hormone signaling (Liu and Chen, 2009), abiotic stress responses (Lu and Huang, 2008; Sunkar et al., 2007), and immune responses (Katiyar-Agarwal and Jin, 2010; Lu et al., 2008; Voinnet, 2008). Similarly, numerous studies have revealed the involvement of specific miRNAs in plant responses to biotic and abiotic stresses. For example, the expression of
Previously we reported that
Seedlings of
Dr. Zhu kindly provided the seeds of wild type (Col-
For drought treatments, 3-week-old plants were treated with natural drought (water was withheld). After 12 days without watering, the drought-treated plants were re-watered, and recovery was checked after 1 day. Drought experiments were repeated five times and at least 7 plants for each individual line were used in each repeated experiment and one representative picture was shown.
The rate of water loss by the leaves was measured. The shoots of 4-week-old plants were detached from the root, and weighed immediately. The shoots were placed in a covered plate at room temperature and weighed at various time intervals. The loss of fresh weight was calculated on the basis of the initial weight of the plant. At least three biological replicates for each sample were used for water loss assays.
RNA was extracted from seedlings using Plant RNA Reagent (Invitrogen, USA) following the supplier’s instructions. For detection of
For detection of
For RT-PCR, total RNA was isolated using an RNaeasy Kit (Qiagen, USA) according to the manufacturer’s instructions. Total RNA was treated with DNase I (Qiagen, USA) to remove genomic DNA contamination. The first-strand cDNA was synthesized using 2 μg total RNA with a cDNA synthesis kit (Invitrogen, USA), and subjected to RT-PCR analysis for examination of gene expression.
Quantitative real-time PCR (qRT-PCR) was used to assay gene expression levels with a CFX384TM Real-Time PCR Detection System (Bio-Rad, USA) following a standard protocol. The QuantiSpeed SYBR kit (PhileKorea, Korea) was used for 20 μl PCR reactions as follows: 50°C for 2 min, 95°C for 2 min, and 40 cycles of 95°C for 5 s and 60°C for 30 s. The relative expression levels of all samples were automatically calculated and analyzed three times by CFX Manager software (Bio-Rad, USA). The specific primers used in RT-PCR and qRT-PCR analysis are described in Supplementary Table 2.
Transgenic plants of
Plant microRNA database (PMRD;
Previously we showed that
To further investigate the regulation of
In
We obtained two
We further examined the response of miR399f-OE plants to ABA treatment by measuring the number of green cotyledons after seed germination (Figs. 4C and 4D). The seeds of WT and miR399f-OE plants were germinated on MS media containing 0 to 1 ?M ABA and grown for 5 days. The seeds of WT and miR399f-OE plants showed different responses to ABA treatment. At 0.3 ?M ABA, approximately 82% of miR399f-OE #15 seedlings developed green cotyledons, compared to approximately 62% of WT seedlings. The difference was more obvious at higher concentrations of ABA. At 1 ?M ABA, the number of miR399f-OE #15 seedlings with green cotyledons was 2.78-fold higher than that of WT seedlings.
In contrast to their tolerance of NaCl and ABA, miR399f-OE plants were more sensitive to drought than WT plants. Three-week-old WT and miR399f-OE plants were subjected to drought stress for 12 days and then re-watered. Under drought conditions, most WT and miR399f-OE plants withered, but one day after re-watering, WT plants resumed growth, whereas miR399f-OE plants had not fully recovered (Fig. 4E). To further confirm the response to drought stress, we examined water loss of WT and miR399f-OE plants, using detached rosette leaves of 4-week-old plants and placing them on petri dishes at room temperature. Water loss proceeded more quickly from leaves of miR399f-OE plants than from WT leaves (Fig. 4F). At 6 h after detachment, the leaves of miR399f-OE plants lost almost 74% of their water, while WT leaves lost only 51%. Together, these results indicated that
The post-transcriptional activity of
The expression of stress-responsive genes is remarkably impaired in the
Abiotic stresses affect various physiological processes in plant development, such as seedling growth and seed germination. Exposure to different abiotic stresses can lead to similar responses in plants. Moreover, different kinds of stresses can trigger responses through the induction of similar types of miRNAs (Sunkar and Zhu, 2004). This suggests that plants share common signaling pathways that act in different abiotic stress responses. The relevant miRNAs are either up- or down-regulated after exposure to stress treatments that influence plant growth and developmental processes (Lu and Huang, 2008). The role of
Several miRNAs function in the ABA-mediated stress response (Chen et al., 2012; Jia et al., 2009; Reyes and Chua, 2007). Some studies suggested a genetic connection between miRNAs and ABA-mediated stress responses (Kim et al., 2010; Song et al., 2013). Consistent with our results indicating the involvement of
Plant responses to various stresses are associated with multiple transcriptional cascades mediated by miRNAs (Lu and Huang, 2008; Sunkar et al., 2007). Identification of direct down-stream target genes regulated by miRNAs in each of these cascades is crucial for understanding miRNA-mediated plant responses to stresses. Through our
While the role of
Overall, the present study identified a biological function of
In summary, we provide the first evidence of the involvement of
Mol. Cells 2016; 39(2): 111-118
Published online February 29, 2016 https://doi.org/10.14348/molcells.2016.2188
Copyright © The Korean Society for Molecular and Cellular Biology.
Dongwon Baek1,3, Hyun Jin Chun1,3, Songhwa Kang1, Gilok Shin1, Su Jung Park1, Hyewon Hong1, Chanmin Kim1, Doh Hoon Kim2, Sang Yeol Lee1, Min Chul Kim1,*, and Dae-Jin Yun1,*
1Division of Applied Life Science (BK21 Plus Program), Plant Molecular Biology and Biotechnology Research Center, Gyeongsang National University, Jinju 660-701, Korea, 2College of Life Science and Natural Resources, Dong-A University, Busan 604-714, Korea
Correspondence to:*Correspondence: djyun@gnu.ac.kr (DJY); mckim@gnu.ac.kr (MCK)
Keywords: ABA, abiotic stress, arabidopsis, drought, microRNA, salt
During growth and development, plants encounter a wide array of environmental stresses that trigger physiological and genetic responses (Chinnusamy and Zhu, 2009; Cushman and Bohnert, 2000). In addition, primary stresses lead to secondary stresses such as oxidative stress and thermal shock. Accordingly, plants have evolved various response mechanisms that help them adapt or acclimate to the stresses (Yamaguchi-Shinozaki and Shinozaki, 2006). A large proportion of plant genes are regulated by biotic (e.g., bacterial pathogens, virus, fungi, insects, and nematodes) (Brotman et al., 2012; Fagard et al., 2007) and abiotic stresses (e.g., drought, soil salinity, extreme temperatures, and heavy metals) (Chao et al., 2005; Si et al., 2009). Various cellular processes, such as RNA processing and post-transcriptional or even post-translational modifications, participate in regulation of the expression of genes in response to biotic and abiotic stresses.
MicroRNAs (miRNAs) can repress gene expression at the post-transcriptional level in plants (Bartel, 2004; Mallory and Vaucheret, 2006). MiRNAs are generally generated via a multistep process associated with the activation of
Recent studies have shown that plants respond to environmental stresses by modulating gene expression at post-transcriptional levels via miRNAs. MiRNAs act in a wide variety of metabolic and biological processes during plant hormone signaling (Liu and Chen, 2009), abiotic stress responses (Lu and Huang, 2008; Sunkar et al., 2007), and immune responses (Katiyar-Agarwal and Jin, 2010; Lu et al., 2008; Voinnet, 2008). Similarly, numerous studies have revealed the involvement of specific miRNAs in plant responses to biotic and abiotic stresses. For example, the expression of
Previously we reported that
Seedlings of
Dr. Zhu kindly provided the seeds of wild type (Col-
For drought treatments, 3-week-old plants were treated with natural drought (water was withheld). After 12 days without watering, the drought-treated plants were re-watered, and recovery was checked after 1 day. Drought experiments were repeated five times and at least 7 plants for each individual line were used in each repeated experiment and one representative picture was shown.
The rate of water loss by the leaves was measured. The shoots of 4-week-old plants were detached from the root, and weighed immediately. The shoots were placed in a covered plate at room temperature and weighed at various time intervals. The loss of fresh weight was calculated on the basis of the initial weight of the plant. At least three biological replicates for each sample were used for water loss assays.
RNA was extracted from seedlings using Plant RNA Reagent (Invitrogen, USA) following the supplier’s instructions. For detection of
For detection of
For RT-PCR, total RNA was isolated using an RNaeasy Kit (Qiagen, USA) according to the manufacturer’s instructions. Total RNA was treated with DNase I (Qiagen, USA) to remove genomic DNA contamination. The first-strand cDNA was synthesized using 2 μg total RNA with a cDNA synthesis kit (Invitrogen, USA), and subjected to RT-PCR analysis for examination of gene expression.
Quantitative real-time PCR (qRT-PCR) was used to assay gene expression levels with a CFX384TM Real-Time PCR Detection System (Bio-Rad, USA) following a standard protocol. The QuantiSpeed SYBR kit (PhileKorea, Korea) was used for 20 μl PCR reactions as follows: 50°C for 2 min, 95°C for 2 min, and 40 cycles of 95°C for 5 s and 60°C for 30 s. The relative expression levels of all samples were automatically calculated and analyzed three times by CFX Manager software (Bio-Rad, USA). The specific primers used in RT-PCR and qRT-PCR analysis are described in Supplementary Table 2.
Transgenic plants of
Plant microRNA database (PMRD;
Previously we showed that
To further investigate the regulation of
In
We obtained two
We further examined the response of miR399f-OE plants to ABA treatment by measuring the number of green cotyledons after seed germination (Figs. 4C and 4D). The seeds of WT and miR399f-OE plants were germinated on MS media containing 0 to 1 ?M ABA and grown for 5 days. The seeds of WT and miR399f-OE plants showed different responses to ABA treatment. At 0.3 ?M ABA, approximately 82% of miR399f-OE #15 seedlings developed green cotyledons, compared to approximately 62% of WT seedlings. The difference was more obvious at higher concentrations of ABA. At 1 ?M ABA, the number of miR399f-OE #15 seedlings with green cotyledons was 2.78-fold higher than that of WT seedlings.
In contrast to their tolerance of NaCl and ABA, miR399f-OE plants were more sensitive to drought than WT plants. Three-week-old WT and miR399f-OE plants were subjected to drought stress for 12 days and then re-watered. Under drought conditions, most WT and miR399f-OE plants withered, but one day after re-watering, WT plants resumed growth, whereas miR399f-OE plants had not fully recovered (Fig. 4E). To further confirm the response to drought stress, we examined water loss of WT and miR399f-OE plants, using detached rosette leaves of 4-week-old plants and placing them on petri dishes at room temperature. Water loss proceeded more quickly from leaves of miR399f-OE plants than from WT leaves (Fig. 4F). At 6 h after detachment, the leaves of miR399f-OE plants lost almost 74% of their water, while WT leaves lost only 51%. Together, these results indicated that
The post-transcriptional activity of
The expression of stress-responsive genes is remarkably impaired in the
Abiotic stresses affect various physiological processes in plant development, such as seedling growth and seed germination. Exposure to different abiotic stresses can lead to similar responses in plants. Moreover, different kinds of stresses can trigger responses through the induction of similar types of miRNAs (Sunkar and Zhu, 2004). This suggests that plants share common signaling pathways that act in different abiotic stress responses. The relevant miRNAs are either up- or down-regulated after exposure to stress treatments that influence plant growth and developmental processes (Lu and Huang, 2008). The role of
Several miRNAs function in the ABA-mediated stress response (Chen et al., 2012; Jia et al., 2009; Reyes and Chua, 2007). Some studies suggested a genetic connection between miRNAs and ABA-mediated stress responses (Kim et al., 2010; Song et al., 2013). Consistent with our results indicating the involvement of
Plant responses to various stresses are associated with multiple transcriptional cascades mediated by miRNAs (Lu and Huang, 2008; Sunkar et al., 2007). Identification of direct down-stream target genes regulated by miRNAs in each of these cascades is crucial for understanding miRNA-mediated plant responses to stresses. Through our
While the role of
Overall, the present study identified a biological function of
In summary, we provide the first evidence of the involvement of
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