Next Article in Journal
Multi-Omics Approaches and Resources for Systems-Level Gene Function Prediction in the Plant Kingdom
Next Article in Special Issue
Full-Length Transcriptome Sequencing Analysis and Characterization of WRKY Transcription Factors Responsive to Cadmium Stress in Arabis paniculata
Previous Article in Journal
Chemical Constituents and Their Production in Mexican Oaks (Q. Rugosa, Q. Glabrescens and Q. Obtusata)
Previous Article in Special Issue
High Levels of Zinc Affect Nitrogen and Phosphorus Transformation in Rice Rhizosphere Soil by Modifying Microbial Communities
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Synergistic Interaction between Copper and Nitrogen-Uptake, Translocation, and Distribution in Rice Plant

1
Microelement Research Center, Huazhong Agricultural University, Wuhan 430070, China
2
College of Resources and Environment, Huazhong Agricultural University, Wuhan 430070, China
*
Author to whom correspondence should be addressed.
Plants 2022, 11(19), 2612; https://doi.org/10.3390/plants11192612
Submission received: 13 September 2022 / Revised: 28 September 2022 / Accepted: 29 September 2022 / Published: 4 October 2022
(This article belongs to the Special Issue Microelements in Plant and Soil)

Abstract

:
Interactions among nutrients have been widely recognized in plants and play important roles in crop growth and yield formation. However, the interplay of Cu and N in rice plants is not yet clear. In this study, rice plants were grown with different combinations of Cu and N supply. The effects of Cu-N interaction on the growth, yield production, Cu and N transport, and gene expression levels were analyzed. The results showed that the effect of N supply on rice growth and yield formation was more pronounced than that of Cu supply. The Cu supply significantly improved the uptake of N (by 9.52–30.64%), while the N supply significantly promoted the root-to-shoot translocation of Cu (by 27.28–38.45%) and distributed more Cu (1.85–19.16%) into the shoots and leaves. The results of qRT-PCR showed that +Cu significantly up-regulated the expression levels of both NO3 and NH4+ transporter genes OsNRTs and OsAMTs, including OsNRT1.1B, OsNRT2.1, OsNRT2.3a, OsNRT2.4, OsAMT1.2, OsAMT1.3, and OsAMT3.1. Meanwhile, +N significantly up-regulated the expression levels of Cu transporter genes OsHMA5 and OsYSL16. In addition, the supply of Cu up-regulated the expression levels of OsGS1;2, OsGS2, and OsNADH-GOGAT to 12.61-, 6.48-, and 6.05-fold, respectively. In conclusion, our study demonstrates a synergistic effect between Cu and N in rice plants. It is expected that our results would be helpful to optimize the application of N and Cu fertilizers in agriculture.

1. Introduction

Nitrogen (N) is a key essential macronutrient required for healthy plant growth and development, which is often a major limiting factor for crop yield production in agriculture [1,2]. N is the constituent of key cell molecules such as nucleic acids, amino acids, chlorophyll, ATP, and plant hormones. Therefore, N is important for many biological processes including photosynthesis, carbon metabolism, and amino acid and protein synthesis [2,3]. A lack of N may have a severe impact on plant growth and development, such as root branching, old leaf chlorosis, increased root-to-shoot ratio, reduced growth and photosynthesis, and fewer seed formation [4,5,6]. Nitrate (NO3) and ammonium (NH4+) are two major forms of N that are absorbed by plant roots from the growth medium. Plants uptake and transport NO3 through nitrate transporters (NRTs), while they uptake and transport NH4+ through ammonium transporters (AMTs) [3]. After absorbing by the plant root, NO3 can be reduced into NH4+ through nitrate reductase (NR) and nitrite reductase (NiR). Then, the NH4+ is assimilated into amino acids for protein synthesis through the glutamine synthetase (GS)/glutamate synthase (GOGAT) cycle [1,7].
Copper (Cu) is one of the essential micronutrients for plant growth and development. Cu is also involved in multiple biological processes, such as photosynthesis, oxidative stress resistance, and ethylene perception [8,9,10]. Cu deficiency may cause specific symptoms in plants, including distortion or whitening of young leaves, apical meristem damage, and decreased seed setting and grain yield [8,9]. The Cu transporter (COPT), heavy-metal ATPase (HMA), yellow stripe-like protein (YSL), and Cu chaperones are reported to be the main transporters and proteins involved in the uptake, root-to-shoot translocation, distribution, and redistribution of Cu in plants [11,12,13,14,15,16].
To date, a large number of studies have revealed strong interactions existing between different nutrients that changing one or more nutrients in the growth medium may affect many other nutrients in plants. Recently, several studies have reported the synergistic interactions between N and other nutrients in plants. For example, the phosphate starvation response is strongly and actively controlled by N provision, and PHR1 (phosphate starvation response 1), PHO2 (phosphate overaccumulation 2), and NRT1.1 (nitrate transporter 1.1) are the major components that integrate N and phosphorus (P) signals in Arabidopsis, rice, and wheat [17]. In rice, the supply of potassium (K) increased N use efficiency by promoting the transformation of storage N to photosynthetic N in the leaves [18]. Molybdenum (Mo) plays a key role in both N uptake and assimilation in winter wheat. The contents of nitrite, ammonium, amino acids, and proteins were significantly increased by the application of Mo [19,20]. Moreover, a markedly synergistic effect of the co-application of N and boron (B) on N uptake, nitrogen use efficiency, and yield production has been shown in rapeseed under B-deficient conditions [21]. Zinc (Zn) and N can also synergistically act in rice plant. The co-supply of Zn and N significantly promoted the root-to-shoot translocation and preferential distribution of both N and Zn, thereafter improving the yield production in rice [22].
Rice is the main staple food with a total planting area of about 30.3 million hectares and feeding > 65% of the population in China [23,24]. Because of the growing population, limited arable land, climate vulnerability, environmental degradation, and low resource-use efficiency, much more effort is needed to improve the rice yield production and ensure food security in China than ever before [25,26,27]. In the last few decades, large amounts of N fertilizers have been applied to improve crop yield in China. However, the N use efficiency in crops is still relatively low, which only accounts for 30–50% in rice [27]. Therefore, increasing crop N use efficiency is still a critical issue in China. Nowadays, the concentration of Cu in agricultural soil has been elevated in various regions, as Cu is always added with pesticide and co-fertilized with other fertilizers, or added to soils by mining and smelting activities and industrial wastewater and solids [28,29,30,31,32]. Hence, in order to know how the co-existence of Cu and N affects the crop growth and yield production, we planted rice plants in both solutions and soils with different combinations of Cu and N supply. The growth phenotype, yield production, uptake, translocation, and distribution of Cu and N were studied to reveal the synergistic effect between Cu and N in rice plant. In addition, the expression levels of genes involved in Cu and N transport, and N reduction and assimilation were analyzed to reveal the underlying mechanism. Our study demonstrates a synergistic effect between Cu and N in rice plant. It is expected that our results would be helpful to optimize the application of N and Cu fertilizers in agriculture.

2. Results

2.1. Growth Phenotype of Rice Plant under the Combined Applications of Cu and N

To assess the effect of different combinations of Cu and N on rice growth, plants were grown in solutions with different combinations of Cu and N supply (Figure 1a, Supplementary Figure S1a–c). The root length gradually decreased with increasing levels of N under -Cu and +Cu conditions, but not under ++Cu conditions, and ++Cu significantly decreased the root length under all three N conditions (Figure 1b). Quite different results were shown in the plant height, shoot dry weight, and leaf SPAD (soil plant analysis development) value, which gradually increased with increasing levels of N under all three Cu conditions (Figure 1c,e; Supplementary Figure S1d). However, there was little effect of Cu on the plant height, shoot dry weight, and leaf SPAD value, except that the shoot dry weight significantly increased with increasing levels of Cu under -N conditions (Figure 1e). The root dry weight did not show significant differences under different combinations of Cu and N, except that it increased by +Cu treatment under -N conditions (Figure 1d).

2.2. Cu Improves the Uptake of N in Rice Plant

To investigate the effect of Cu on N transport in rice plant, we determined the N concentration in the root, basal node, and shoot samples, and calculated the N accumulation, root uptake capacity, and root-to-shoot translocation and distribution under different combinations of Cu and N supply. There was no significant effect of Cu on N concentration in the root, basal node, and shoot under -N, +N, or ++N conditions, except that a higher N concentration in the root after +Cu treatment under +N conditions, higher N concentration in the basal node after +Cu and ++Cu treatments under ++N conditions, and higher N concentration in the shoot after +Cu and ++Cu treatments under +N conditions were observed (Figure 2a). The N accumulation in both the basal node and shoot gradually increased with increasing levels of Cu under all three N conditions, while little effect of Cu on the N accumulation in the root was observed (Figure 2b). The supply of N significantly improved the root uptake capacity of N under various Cu conditions, while the supply of Cu clearly increased the root uptake capacity of N under +N and ++N conditions, but not under -N conditions (Figure 3a). Compared to -Cu treatments, the root uptake capacity of N increased by 30.31% and 10.56% after +Cu and ++Cu treatments, respectively, under +N conditions, and increased by 13.71% and 18.88% after +Cu and ++Cu treatments, respectively, under ++N conditions (Figure 3a). The supply of N significantly improved the plant uptake of N under various Cu conditions (Figure 3b). Simultaneously, the supply of Cu also significantly increased the plant uptake of N under all three N conditions (Figure 3b). Compared to -Cu treatment, the uptake of N in rice plant increased by 9.52% and 24.17% after +Cu and ++Cu treatments, respectively, under -N conditions, increased by 30.64% and 17.70% after +Cu and ++Cu treatments, respectively, under +N conditions, and increased by 10.05% and 18.86% after +Cu and ++Cu treatments, respectively, under ++N conditions (Figure 3b). The supply of N slightly improved the root-to-shoot translocation of N, while the supply of Cu did not affect the root-to-shoot translocation of N (Figure 3c). However, the distribution of N in different organs did not show any significant changes under different combinations of Cu and N supply (Figure 3d). These results suggest that the effect of Cu-N interaction on N uptake is more pronounced than the effect on the root-to-shoot translocation and distribution of N in rice plant. Our results demonstrate that the Cu supply can improve the uptake of N in rice plant, but not the root-to-shoot translocation of N or the distribution of N in each organ.

2.3. N Promotes the Translocation and Distribution of Cu in Rice Plant

There was little effect of N on the Cu concentration in the root, basal node, and shoot under -Cu, +Cu, or ++Cu conditions that only a lower Cu concentration in the root after +N treatment under ++Cu conditions, a lower Cu concentration in the basal node after +N and ++N treatments under +Cu and ++Cu conditions, but a higher Cu concentration in the shoot after ++N treatment under ++Cu conditions were observed (Figure 4a). The Cu accumulation in the root and basal node gradually increased with increasing N levels under -Cu conditions, and the Cu accumulation in the shoot gradually increased with increasing N levels under all three Cu conditions, while no significant differences were shown in the Cu accumulation of the root and basal node among different N treatments under either +Cu or ++Cu conditions (Figure 4b). The N supply did not affect the root uptake capacity of Cu under any Cu condition, except that a higher root uptake capacity of Cu was shown after ++N treatment under ++Cu conditions (Figure 5a). Similarly, the N supply did not affect the plant uptake of Cu under +Cu and ++Cu conditions, while an increasing plant uptake of Cu was shown with increasing N levels under -Cu conditions (Figure 5b). Interestingly, the N supply significantly increased the root-to-shoot translocation of Cu under +Cu and ++Cu conditions, but not under -Cu conditions (Figure 5c). Compared to -N treatment, the root-to-shoot translocation of Cu increased by 27.28% and 38.45% after +N and ++N treatments, respectively, under +Cu conditions, and increased by 29.41% and 34.27% after +N and ++N treatments, respectively, under ++Cu conditions (Figure 5c). The N supply also promoted the distribution of Cu in the rice shoot under all three Cu conditions (Figure 5d). Compared to -N treatment, the distribution of Cu in the rice shoot increased 3.87% and 1.85% after +N and ++N treatments, respectively, under -Cu conditions, increased 13.41% and 19.16% after +N and ++N treatments, respectively, under +Cu conditions, and increased 6.72% and 9.72% after +N and ++N treatments, respectively, under ++Cu conditions (Figure 5d). Our results demonstrate that the N supply is beneficial for distributing more Cu to the shoot, which may promote the growth of rice plant.

2.4. Cu Up-Regulated the Expression Levels of Genes Involved in N Transport, Reduction, and Assimilation

To understand the molecular mechanism of the effect of Cu supply on N uptake, reduction, and assimilation, we analyzed the expression levels of key genes involved in N transport, reduction, and assimilation in both root and shoot samples under different combinations of Cu and N supply. The results showed that the expression levels of most of the nitrate and ammonium transport genes as well as nitrate reduction and ammonium assimilation genes were up-regulated by Cu addition, except that the expression levels of two low-affinity nitrate transport genes, OsNRT1.1A and OsNRT1.1B, were down-regulated by Cu addition in the root under -N conditions (Figure 6a–c). The effect of Cu on the expression of nitrate and ammonium transport genes was more pronounced in the root than in the shoot. For example, the expression levels of OsNRT2.1 and OsNRT2.3a increased to 12.41-fold and 5.16-fold, respectively, after +Cu treatment in the root under -N conditions, while the expression levels of OsNRT1.1B and OsNRT2.4 increased to 13.85-fold and 6.89-fold, respectively, after +Cu treatment in the root under +N conditions (Figure 6a). The expression level of OsAMT1.2 increased to 8.39-fold after +Cu treatment in the root under -N conditions, and the expression levels of OsAMT1.2, OsAMT1.3, and OsAMT3.1 increased to 6.25-fold, 5.11-fold, and 5.89-fold, respectively, after +Cu treatment in the root under +N conditions (Figure 6b). The effect of Cu on the expression of ammonium assimilation genes was more pronounced than the nitrate reduction genes. For example, the expression level of OsGS1;2 increased to 12.62-fold after +Cu treatment in the root under -N conditions, the expression level of OsNADH-GOGAT increased to 6.05-fold after +Cu treatment in the root under +N conditions, and the expression level of GS2 increased to 6.48-fold after +Cu treatment in the shoot under -N conditions (Figure 6c).

2.5. N Up-Regulated the Expression Levels of Genes Involved in Cu Transport

The results of the expression analysis of genes involved in the Cu transport also showed that the expression levels of most of the Cu transport genes were up-regulated by N addition. The effect of N on the expression of Cu transport genes was more pronounced in the root than in the shoot. For example, the expression levels of OsCOPT1 and OsHMA5 increased to 3.88-fold and 22.98-fold, respectively, after +N treatment in the root under -Cu conditions, and the expression levels of OsCOPT7, OsHMA5, and OsYSL16 increased to 8.59-fold, 3.83-fold, and 3.73-fold, respectively, after +N treatment in the root under +Cu conditions (Figure 6d). Only the expression level of OsHMA5 increased to 4.16-fold after +N treatment in the shoot under -Cu conditions (Figure 6d).

2.6. Yield Evaluation of Rice Plant under the Combined Applications of Cu and N

To investigate the effect of different combinations of Cu and N on rice yield formation, plants were grown in soils with different combinations of Cu and N supply (Figure 7a, Supplementary Figure S2a). The N supply significantly increased the straw dry weight, grain yield, and number of effective panicles under both -Cu and +Cu conditions, while it only increased the plant height, panicle length, fertility, and seed number per panicle under -Cu conditions, but it did not affect the 1000-seed weight under either -Cu or +Cu conditions (Figure 7b,c; Supplementary Figure S2b–g). However, there was less impact of Cu on the plant growth and yield formation. The Cu supply could increase the panicle length, fertility, and seed number per panicle, but significantly decreased the 1000-seed weight and number of effective panicles under all three N conditions (Supplementary Figure S2c–g). The Cu supply only increased the plant height and grain yield under -N conditions, and no significant changes were observed in straw dry weight after Cu supply under any treatment of N (Figure 7c).

2.7. N Affects The Concentration, Accumulation, and Distribution of Cu in Rice Plant at Mature Stage

Unexpectedly, the Cu supply did not affect the N concentration, accumulation, and distribution in rice plants at the mature stage (data not shown). However, the N supply significantly affected the Cu concentration, accumulation, and distribution in rice plants at this growth stage (Figure 8). The Cu concentrations in all organs, including new leaf, old leaf, node, internode, spike stalk, and grain, gradually increased with the increasing levels of N under both -Cu and +Cu conditions (Figure 8a). Compared to -N treatment, the Cu accumulation in rice plant increased by 152.21% and 166.35% after +N and ++N treatments, respectively, under -Cu conditions, and increased by 37.72% and 138.03% after +N and ++N treatments, respectively, under +Cu conditions (Figure 8b). The N supply significantly increased the Cu distribution in leaves but decreased the Cu distribution in rice grains under both -Cu and +Cu conditions (Figure 8c). Compared to -N treatment, the Cu distribution in leaves increased 6.94% and 4.03% after +N and ++N treatments, respectively, under -Cu conditions, and increased 12.02% and 10.37% after +N and ++N treatments, respectively, under +Cu conditions (Figure 8c). The Cu distribution in grains decreased 10.73% and 7.83% after +N and ++N treatments, respectively, under -Cu conditions, and decreased 14.06% and 15.07% after +N and ++N treatments, respectively, under +Cu conditions (Figure 8c). Our results suggest that N supply improves both the concentration and accumulation of Cu in rice plant, and also promotes the distribution of Cu in the shoot at the mature stage, which may be beneficial for the yield production.

3. Discussion

Interactions among nutrients have been widely recognized in plants. Previous studies have shown that synergistic effects between N and several other nutrients, such as P, K, Mo, B, and Zn, existed in crops [17,18,19,20,21,22]. Here, we studied the interplay between Cu and N in rice plant. Our results also showed a synergistic effect between Cu and N existing in rice plant. The supply of Cu improved the uptake of N, while the supply of N promoted the root-to-shoot translocation of Cu and distributed more Cu into shoots and leaves, which is beneficial for the plant growth and yield production in rice (Figure 1, Figure 3, Figure 5 and Figure 7). However, no significant impact of N supply on Cu concentration in rice plant was observed in our study, while Cai et al. reported that the foliar Cu concentration increased with the addition of N in forbs and grasses [33]. Similarly, no significant impact of Cu supply on the N concentration in rice plant was observed in our study, while Zhou et al. reported that the application of N increased the Cu content in the roots of R. communis [34]. The interactive effect between Cu and N may be various in plants with different application levels of Cu or N. The negative impact of N supply (280 kg ha−1) on Cu uptake was observed in N. nivea grown in Cu-contaminated soils [35]. Furthermore, high levels of Cu inhibited the N uptake and upward translocation in Chinese cabbage, and influenced N metabolism in rice plant [36,37].
NRTs and AMTs are the two major gene families encoding the membrane transporters contributed for NO3 and NH4+ uptake and transportation in plants. In our study, the expression levels of OsNRT2.1 and OsNRT2.3a significantly increased (>5-fold) after +Cu treatment in the root under -N conditions, while the expression levels of OsNRT1.1B and OsNRT2.4 significantly increased (>5-fold) after +Cu treatment in the root under +N conditions (Figure 6a). OsNRT2.1 and OsNRT2.3a are two high-affinity nitrate transporter genes mainly expressed in the rice root and involved in NO3 uptake and long-distance transport, respectively, under low-N conditions [38,39]. OsNRT1.1B is a low-affinity nitrate transporter gene mainly expressed in rice roots and contributed to NO3 uptake under N-sufficient conditions [40], while OsNRT2.4 behaves as a dual-affinity nitrate transporter and plays important roles in NO3 uptake under both N-deficient and -sufficient conditions [41]. Moreover, the expression level of OsAMT1.2 increased to 8.39-fold after +Cu treatment in the root under -N conditions, and the expression levels of OsAMT1.2, OsAMT1.3, and OsAMT3.1 increased over 5-fold after +Cu treatment in the root under +N conditions (Figure 6b). OsAMT1;2 is a root-specific and ammonium-inducible expressed gene, whereas OsAMT1;3 is also expressed specifically in roots but repressed by N, both of them being involved in NH4+ uptake in rice plant [42,43,44,45]. Our results clearly showed that the Cu supply significantly up-regulated the expression levels of OsNRTs and OsAMTs in rice plant, and the impact was more pronounced in the root than in the shoot (Figure 6a,b). Therefore, the higher expression levels of these N transporter genes in the root may contribute to the improved N uptake in rice plant after Cu addition.
In addition to N transport genes, our results also showed that the Cu supply significantly up-regulated the expression levels of genes involved in nitrate reduction and ammonium assimilation, and the impact of Cu on the expression of ammonium assimilation genes was more pronounced than the nitrate reduction genes (Figure 6c). The expression level of OsGS1;2 and OsNADH-GOGAT significantly increased after +Cu treatment in the root under -N and +N conditions, respectively, and the expression level of GS2 significantly increased after +Cu treatment in the shoot under -N conditions (Figure 6c). OsGS1;2 and OsNADH-GOGAT are two root-expressed genes encoding the cytosolic glutamine synthetase and glutamate synthase, respectively, which are important for the primary ammonium assimilation in rice root [46,47,48], while OsGS2 is a leaf-expressed gene encoding the chloroplastic glutamine synthetase and is a main factor involved in primary ammonium assimilation in rice leaves [46,49]. Our results suggested that the Cu supply might also promote nitrate reduction and ammonium assimilation in rice plant through up-regulating the expression levels of OsGS1;2 and OsNADH-GOGAT in the root as well as the expression level of OsGS2 in rice leaf.
OsHMA5 is a plasma-membrane-localized heavy-metal ATPase, which is highly expressed in the root pericycle cells and xylem region of diffuse vascular bundles in nodes, and functions in loading Cu to the xylem of the roots, and translocating Cu to aboveground organs [14]. OsYSL16 is a Cu-nicotianamine transporter, which is highly expressed in the phloem of nodes and vascular tissues of leaves, and functions in delivering Cu to the developing young tissues in rice plant [15,50]. In our study, the expression levels of OsHMA5 increased to 22.98-fold and 4.16-fold after +N treatment in the root and shoot, respectively, under -Cu conditions, and the expression levels of OsHMA5 and OsYSL16 increased to 8.59-fold and 3.73-fold, respectively, after +N treatment in the root under +Cu conditions (Figure 6d). These results suggested that the N supply promoted the root-to-shoot translocation of Cu and distribution of more Cu into the shoots and leaves mainly through up-regulating the expression levels of OsHMA5 and OsYSL16. Although a significantly higher expression level of OsCOPT7 (8.59-fold) was also observed in the rice root after +N treatment under +Cu conditions (Figure 6d), the basal expression level of OsCOPT7 in the rice root is relatively low as reported by Yuan et al. [51], which means that the function of OsCOPT7 in Cu uptake is relatively weak, and that is why the uptake of Cu was not affected by N supply in our study.
In conclusion, our study showed a synergistic effect between Cu and N in rice plant. The Cu supply improved the uptake of N through up-regulating the expression levels of both NO3 and NH4+ transporter genes OsNRTs and OsAMTs, while the N supply promoted the root-to-shoot translocation of Cu and distributed more Cu into the shoots and leaves through up-regulating the expression levels of Cu transporter genes OsHMA5 and OsYSL16. In addition, the Cu supply significantly up-regulated the expression levels of primary ammonium assimilation genes OsGS1;2, OsGS2, and OsNADH-GOGAT, which may enhance the N metabolic level in rice plant. Although our results may be helpful to optimize the application of N and Cu fertilizers in agriculture, the field experiment is still needed in the future to determine appropriated amounts of N and Cu fertilizers for achieving the maximum N use efficiency and yield production.

4. Materials and Methods

4.1. Hydroponic Culture

The rice cultivar Guangliangyou 35, one of the most widely planted hybrid indica rice cultivars in Hubei Province, China, was used in this study. The experiment was conducted in Huazhong Agricultural University, Wuhan, China (30°46′ N, 114°36′ E) in March 2021. For hydroponic culture, seeds were soaked in water at 30 °C in the dark for three days and then transferred to a net floating on a 0.5 mM CaCl2 solution. After a week, the seedlings were transferred to a Yoshida solution containing 1.44 mM NH4NO3, 0.3 mM NaH2PO4, 0.5 mM K2SO4, 1.0 mM CaCl2, 1.6 mM MgSO4, 0.17 mM Na2SiO3, 50 μM Fe-EDTA, 0.06 μM (NH4)6Mo7O24, 15 μM H3BO3, 8 μM MnCl2, 0.15 μM CuSO4, 0.15 μM ZnSO4, 29 μM FeCl3, and 40.5 μM citric acid (pH 5.6) [52]. The different treatments of CuSO4 (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and NH4NO3 (-N, 0.144 mM; +N, 1.44 mM; ++N, 7.20 mM) were conducted. Seedlings were grown in a greenhouse at 25 °C to 30 °C under natural light. Solutions were renewed every three days. Three biological replicates with two plants for each replicate were conducted. Three weeks later, the roots were washed three times with 0.5 mM CaCl2. The root, basal node, and shoot samples were harvested for the determination of Cu and N, and the root and shoot samples were harvested for the gene expression analysis by qRT-PCR as described below.

4.2. Pot Experiment

The experiment was conducted in Huazhong Agricultural University, Wuhan, China (30°46′ N, 114°36′ E) from July to October in 2021. For pot experiment, seeds were soaked in water at 30 °C in the dark for three days and then transferred to a net floating on a 0.5 mM solution of CaCl2. After a week, seedlings were transferred to pots containing 10 kg of dry soil, which was fertilized with 0.15 g P2O5 kg−1 soil and 0.2 g K2O kg−1 soil. The different treatments of CuSO4 (-Cu, 0 mg Cu kg−1 soil; +Cu, 50 mg Cu kg−1 soil) and urea (-N, 0 g N kg−1 soil; +N, 0.2 g N kg−1 soil; ++N, 0.4 g N kg−1 soil) were conducted. Seedlings were grown at 25 °C to 35 °C under natural light until maturation. Three biological replicates were conducted. Four rice plants were planted for each biological replicate. At the mature stage, the grain yield was evaluated, and different organs, including the new leaf, old leaf, node, internode, spike stalk, and grain, were harvested for the determination of Cu and N as described below.

4.3. N Determination

The harvested samples were dried in an oven at 70 °C for 5 days. After recording the dry weight, the samples were ground into powder. Amounts of 0.05 g from each sample were subjected to digestion with 3 mL of 98% H2SO4 on a heater at up to 280 °C. In addition, 2-3 drops of H2O2 were added several times until the solution became transparent. The concentration of total N in the digested solution was determined using a flow injection analyzer (FIAstar 5000, FOSSTECATOR, Stockholm, Sweden). The N accumulation was calculated as N concentration × dry weight; the N uptake was calculated as the N accumulation of whole plant; the uptake capacity of N was calculated as the N accumulation of whole plant/root dry weight; the root-to-shoot translocation of N was calculated as the N accumulation in shoot/the N accumulation of whole plant; the N distribution in each organ was calculated as the N accumulation in each organ/the N accumulation of whole plant.

4.4. Cu Determination

The harvested samples were dried in an oven at 70 °C for 5 days. After recording the dry weight, the samples were ground into powder. Amounts of 0.15 g from each sample were subjected to digestion with 3 mL of 11 N HNO3 on a heater at up to 130 °C until the solution became transparent. The concentration of Cu in the digested solution was determined using an atomic absorption spectrophotometer (WFX-ID, RUILI, Beijing, China). The Cu accumulation was calculated as Cu concentration × dry weight; the Cu uptake was calculated as the Cu accumulation of whole plant; the uptake capacity of Cu was calculated as the Cu accumulation of whole plant/root dry weight; the root-to-shoot translocation of Cu was calculated as the Cu accumulation in shoot/the Cu accumulation of whole plant; the Cu distribution in each organ was calculated as the Cu accumulation in each organ/the Cu accumulation of whole plant.

4.5. RNA Extraction and qRT-PCR Analysis

Total RNA was extracted from root and shoot samples using a RNeasy Plant Mini Kit (Yeasen, Shanghai, China) and converted to cDNA using the Rever Tra Ace qPCR RT Master Mix with a gDNA remover (Yeasen, Shanghai, China) following the manufacturer’s protocol. The cDNA was amplified using the SYBR Green Real-Time PCR Master Mix Kit (KAPA, Boston, USA) following the manufacturer’s protocol. The reaction was added with 2.0 μL of cDNA, 0.2 μL of forward primer, 0.2 μL of reverse primer, 5.0 μL of SYBR Green, and 2.6 μL of ddH2O. The quantitative real-time PCR was performed using a Quant Studio TM 6 Flex System (Applied Biosystems, Foster City, CA, USA) with specific gene primers (Supplementary Table S1). The reaction was performed as 95 °C 10 s, 60 °C 20 s, and 72 °C 20 s, for 40 cycles. The relative gene expression levels were normalized using an internal standard (OsUbiquitin) and calculated using the 2−ΔΔCt method with CFX Manager Software (Bio-Rad, CA, USA). The fold changes of N-related genes were calculated as the expression levels of each gene under +Cu conditions/the expression levels of each gene under -Cu conditions; the fold changes of Cu-related genes were calculated as the expression levels of each gene under +N conditions/the expression levels of each gene under -N conditions.

4.6. Statistical Analysis

For statistical analyses, the software of SPSS 19.0 (Statistical Package for the Social Sciences, version of 19.0, Chicago, IL, USA) was used. Analysis of variance (ANOVA) was employed to identify significant differences for each parameter among the treatments of different combined applications of Cu and N at the 5% probability level (p < 0.05). Data are presented as means ± SD with three independent replicates. Significant differences were determined by Tukey’s multiple range test (p < 0.05).

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/plants11192612/s1, Figure S1: Growth phenotype and leaf SPAD value of rice plant grown in solutions with different combinations of Cu and N; Figure S2: Growth phenotype and yield components of rice plant grown in soil with different combinations of Cu and N; Table S1: Primers used in qRT-PCR.

Author Contributions

Conceptualization, X.C. and H.C.; data duration, X.C., H.H., S.H. and B.Z.; formal analysis, X.C.; investigation, X.C. and H.H.; methodology, X.C.; supervision, H.C.; validation, X.C., H.H., S.H. and B.Z.; funding acquisition, H.C.; writing, original draft, X.C.; writing, review and editing, H.C. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Key R&D Program of China, grant number [2021YFD1901203].

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Tabuchi, M.; Abiko, T.; Yamaya, T. Assimilation of ammonium ions and reutilization of nitrogen in rice (Oryza sativa L.). J. Exp. Bot. 2007, 58, 2319–2327. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  2. Frink, C.R.; Waggoner, P.E.; Ausubel, J.H. Nitrogen fertilizer: Retrospect and prospect. Proc. Natl. Acad. Sci. USA 1999, 96, 1175–1180. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  3. Crawford, N.M.; Ford, B.G. Molecular and developmental biology of inorganic nitrogen nutrition. In The Arabidopsis Book; Meyerowitz, E., Somerville, C., Eds.; American Society of Plant Biologists: Rockville, MD, USA, 2002. [Google Scholar]
  4. Good, A.G.; Shrawat, A.K.; Muench, D.G. Can less yield more? Is reducing nutrient input into the environment compatible with maintaining crop production? Trends Plant Sci. 2004, 9, 597–605. [Google Scholar] [CrossRef] [PubMed]
  5. Diaz, C.; Saliba-Colombani, V.; Loudet, O.; Belluomo, P.; Moreau, L.; Daniel-Vedele, F.; Morot-Gaudry, J.-F.; Masclaux-Daubresse, C. Leaf yellowing and anthocyanin accumulation are two genetically independent strategies in response to nitrogen limitation in Arabidopsis thaliana. Plant Cell Physiol. 2006, 47, 74–83. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  6. Ding, L.; Wang, K.J.; Jiang, G.M.; Biswas, D.K.; Xu, H.; Li, L.F.; Li, Y.H. Effects of nitrogen deficiency on photosynthetic traits of maize hybrids released in different years. Ann. Bot. 2005, 96, 925–930. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  7. Lam, H.M.; Coschigano, K.T.; Oliveira, I.C.; Melo-Oliveira, R.; Coruzzi, G.M. The molecular-genetics of nitrogen assimilation into amino acids in higher plants. Annu. Rev. Plant Physiol. Plant Mol. Biol. 1996, 47, 569–593. [Google Scholar] [CrossRef] [PubMed]
  8. Burkhead, J.L.; Reynolds, K.A.; Abdel-Ghany, S.E.; Cohu, C.M.; Pilon, M. Copper homeostasis. New Phytol. 2009, 182, 799–816. [Google Scholar] [CrossRef] [PubMed]
  9. Broadley, M.; Brown, P.; Cakmak, I.; Rengel, Z.; Zhao, F.J. Function of nutrients: Micronutrients. In Mineral Nutrition of Higher Plants; Marschner, P., Ed.; Academic Press: Waltham, MA, USA, 2012. [Google Scholar]
  10. Ravet, K.; Pilon, M. Copper and iron homeostasis in plants: The challenges of oxidative stress. Antioxid. Redox Signal. 2013, 19, 919–932. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  11. Puig, S.; Thiele, D.J. Molecular mechanisms of copper uptake and distribution. Curr. Opin. Chem. Biol. 2002, 6, 171–180. [Google Scholar] [CrossRef]
  12. Puig, S. Function and regulation of the plant COPT family of high-affinity copper transport proteins. Adv. Bot. 2014, 2, 1–9. [Google Scholar] [CrossRef]
  13. Abdel-Ghany, S.E.; Müller-Moulé, P.; Niyogi, K.K.; Pilon, M.; Shikanai, T. Two P-type ATPases are required for copper delivery in Arabidopsis thaliana chloroplasts. Plant Cell 2005, 17, 1233–1251. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  14. Deng, F.; Yamaji, N.; Xia, J.; Ma, J.F. 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. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  15. Zheng, L.; Yamaji, N.; Yokosho, K.; Ma, J.F. YSL16 is a phloem-localized transporter of the copper-nicotianamine complex that is responsible for copper distribution in rice. Plant Cell 2012, 24, 3767–3782. [Google Scholar] [CrossRef] [Green Version]
  16. Shin, L.J.; Yeh, K.C. Overexpression of Arabidopsis ATX1 retards plant growth under severe copper deficiency. Plant Signal. Behav. 2012, 7, 1082–1083. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  17. Medici, A.; Szponarski, W.; Dangeville, P.; Safi, A.; Dissanayake, I.M.; Saenchai, C.; Emanuel, A.; Rubio, V.; Lacombe, B.; Ruffel, S.; et al. Identification of molecular integrators shows that nitrogen actively controls the phosphate starvation response in plants. Plant Cell 2019, 31, 1171–1184. [Google Scholar] [CrossRef]
  18. Hou, W.; Tränkner, M.; Lu, J.; Yan, J.; Huang, S.; Ren, T.; Cong, R.; Li, X. Interactive effects of nitrogen and potassium on photosynthesis and photosynthetic nitrogen allocation of rice leaves. BMC Plant Biol. 2019, 19, 302. [Google Scholar] [CrossRef]
  19. Imran, M.; Sun, X.; Hussain, S.; Ali, U.; Rana, M.S.; Rasul, F.; Saleem, M.H.; Moussa, M.G.; Bhantana, P.; Afzal, J.; et al. Molybdenum-induced effects on nitrogen metabolism enzymes and elemental profile of winter wheat (Triticum aestivum L.) under different nitrogen sources. Int. J. Mol. Sci. 2019, 20, 3009. [Google Scholar] [CrossRef] [Green Version]
  20. Imran, M.; Hu, C.X.; Hussain, S.; Rana, M.S.; Riaz, M.; Afzal, J.; Aziz, O.; Elyamine, A.M.; Ismael, M.A.F.; Sun, X. Molybdenum-induced effects on photosynthetic efficacy of winter wheat (Triticum aestivum L.) under different nitrogen sources are associated with nitrogen assimilation. Plant Physiol. Biochem. 2019, 141, 154–163. [Google Scholar] [CrossRef]
  21. Wang, Y.; Zhao, Z.; Wang, S.; Shi, L.; Xu, F. Genotypic differences in the synergistic effect of nitrogen and boron on the seed yield and nitrogen use efficiency of Brassica napus. J. Sci. Food Agric. 2022, 102, 3563–3571. [Google Scholar] [CrossRef]
  22. Ji, C.; Li, J.; Jiang, C.; Zhang, L.; Shi, L.; Xu, F.; Cai, H. Zinc and nitrogen synergistic act on root-to-shoot translocation and preferential distribution in rice. J. Adv. Res. 2022, 35, 187–198. [Google Scholar] [CrossRef]
  23. Food and Agricultural Organizations of the United Nations. Available online: http://www.fao.org/statistic/en/ (accessed on 9 October 2014).
  24. Zhang, X.; Wang, D.; Fang, F.; Zhen, Y. Food safety and rice production in China. Res. Agric. Mod. 2005, 26, 85–88. [Google Scholar]
  25. Cassman, K.G. Ecological intensification of cereal production systems: Yield potential, soil quality, and precision agriculture. Proc. Natl. Acad. Sci. USA 1999, 96, 5952–5959. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  26. Zhang, F.; Chen, X.; Vitousek, P. An experiment for the world. Nature 2013, 497, 33–35. [Google Scholar] [CrossRef] [PubMed]
  27. Wang, F.; Peng, S. Yield potential and nitrogen use efficiency of China’s super rice. J. Integr. Agric. 2017, 16, 1000–1008. [Google Scholar] [CrossRef] [Green Version]
  28. Chen, Q.; Zhang, X.; Zhang, H.; Christie, P.; Li, X.; Horlacher, D.; Liebig, H.P. Evaluation of current fertilizer practice and soil fertility in vegetable production in the Beijing region. Nutr. Cycl. Agroecosyst. 2004, 69, 51–58. [Google Scholar] [CrossRef] [Green Version]
  29. Sun, Y.; Zhou, Q.; Xie, X.; Liu, R. Spatial, sources and risk assessment of heavy metal contamination of urban soils in typical regions of Shenyang, China. J. Hazard. Mater. 2010, 174, 455–462. [Google Scholar] [CrossRef]
  30. Luo, C.; Liu, C.; Wang, Y.; Liu, X.; Li, F.; Zhang, G.; Li, X. Heavy metal contamination in soils and vegetables near an e-waste processing site, south China. J. Hazard. Mater. 2011, 186, 481–490. [Google Scholar] [CrossRef]
  31. Wu, W.; Wu, P.; Yang, F.; Sun, D.L.; Zhang, D.X.; Zhou, Y.K. Assessment of heavy metal pollution and human health risks in urban soils around an electronics manufacturing facility. Sci. Total Environ. 2018, 630, 53–61. [Google Scholar] [CrossRef]
  32. Yang, Q.; Li, Z.; Lu, X.; Duan, Q.; Huang, L.; Bi, J. A review of soil heavy metal pollution from industrial and agricultural regions in China: Pollution and risk assessment. Sci. Total Environ. 2018, 642, 690–700. [Google Scholar] [CrossRef]
  33. Cai, J.; Weiner, J.; Wang, R.; Luo, W.; Zhang, Y.; Liu, H.; Xu, Z.; Li, H.; Zhang, Y.; Jiang, Y. Effects of nitrogen and water addition on trace element stoichiometry in five grassland species. J. Plant Res. 2017, 130, 659–668. [Google Scholar] [CrossRef]
  34. Zhou, X.; Huang, G.; Liang, D.; Liu, Y.; Yao, S.; Ali, U.; Hu, H. Influence of nitrogen forms and application rates on the phytoextraction of copper by castor bean (Ricinus communis L.). Environ. Sci. Pollut. Res. 2020, 27, 647–656. [Google Scholar] [CrossRef] [PubMed]
  35. Rehman, M.; Saleem, M.H.; Fahad, S.; Maqbool, Z.; Peng, D.; Geng, G.; Liu, L. Medium nitrogen optimized Boehmeria nivea L. growth in copper contaminated soil. Chemosphere 2021, 266, 128972. [Google Scholar] [CrossRef] [PubMed]
  36. Huo, K.; Shangguan, X.; Xia, Y.; Shen, Z.; Chen, C. Excess copper inhibits the growth of rice seedlings by decreasing uptake of nitrate. Ecotoxic. Environ. Saf. 2020, 190, 110105. [Google Scholar] [CrossRef]
  37. Xiong, Z.T.; Liu, C.; Geng, B. Phytotoxic effects of copper on nitrogen metabolism and plant growth in Brassica pekinensis Rupr. Ecotoxic. Environ. Saf. 2006, 64, 273–280. [Google Scholar] [CrossRef]
  38. Katayama, H.; Mori, M.; Kawamura, Y.; Tanaka, T.; Mori, M.; Hasegawa, H. Production and characterization of transgenic rice plants carrying a high-affinity nitrate transporter gene (OsNRT2.1). Breed. Sci. 2009, 59, 237–243. [Google Scholar] [CrossRef] [Green Version]
  39. Tang, Z.; Fan, X.; Li, Q.; Feng, H.; Miller, A.J.; Shen, Q.; Xu, G. Knockdown of a rice stelar nitrate transporter alters long-distance translocation but not root influx. Plant Physiol. 2012, 160, 2052–2063. [Google Scholar] [CrossRef] [Green Version]
  40. Fan, X.; Feng, H.; Tan, Y.; Xu, Y.; Miao, Q.; Xu, G. A putative 6-transmembrane nitrate transporter OsNRT1.1b plays a key role in rice under low nitrogen. J. Integr. Plant Biol. 2016, 58, 590–599. [Google Scholar] [CrossRef] [Green Version]
  41. Wei, J.; Zheng, Y.; Feng, H.; Qu, H.; Fan, X.; Yamaji, N.; Ma, J.F.; Xu, G. OsNRT2.4 encodes a dual-affinity nitrate transporter and functions in nitrate-regulated root growth and nitrate distribution in rice. J. Exp. Bot. 2018, 69, 1095–1107. [Google Scholar] [CrossRef] [Green Version]
  42. Sonoda, Y.; Ikeda, A.; Saiki, S.; von Wirén, N.; Yamaya, T.; Yamaguchi, J. Distinct expression and function of three ammonium transporter genes (OsAMT1;1-1;3) in rice. Plant Cell Physiol. 2003, 44, 726–734. [Google Scholar] [CrossRef] [Green Version]
  43. Lee, S.; Marmagne, A.; Park, J.; Fabien, C.; Yim, Y.; Kim, S.; Kim, T.H.; Lim, P.O.; Masclaux-Daubresse, C.; Nam, H.G. Concurrent activation of OsAMT1;2 and OsGOGAT1 in rice leads to enhanced nitrogen use efficiency under nitrogen limitation. Plant J. 2021, 103, 7–20. [Google Scholar] [CrossRef]
  44. Hao, D.; Yang, S.; Huang, Y.; Su, Y. Identification of structural elements involved in fine-tuning of the transport activity of the rice ammonium transporter OsAMT1;3. Plant Physiol. Biochem. 2016, 108, 99–108. [Google Scholar] [CrossRef] [PubMed]
  45. Bao, A.; Liang, Z.; Zhao, Z.; Cai, H. Overexpressing of OsAMT1-3, a high affinity ammonium transporter gene, modifies rice growth and carbon-nitrogen metabolic status. Int. J. Mol. Sci. 2015, 16, 9037–9063. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  46. Hirel, B.; Gadal, P. Glutamine synthetase in rice: A comparative study of the enzymes from roots and leaves. Plant Physiol. 1980, 66, 619–623. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  47. Funayama, K.; Kojima, S.; Tabuchi-Kobayashi, M.; Sawa, Y.; Nakayama, Y.; Hayakawa, T.; Yamaya, T. Cytosolic glutamine synthetase1;2 is responsible for the primary assimilation of ammonium in rice roots. Plant Cell Physiol. 2013, 54, 934–943. [Google Scholar] [CrossRef] [PubMed]
  48. Tamura, W.; Hidaka, Y.; Tabuchi, M.; Kojima, S.; Hayakawa, T.; Sato, T.; Obara, M.; Kojima, M.; Sakakibara, H.; Yamaya, T. Reverse genetics approach to characterize a function of NADH-glutamate synthase1 in rice plants. Amino Acids 2010, 39, 1003–1012. [Google Scholar] [CrossRef]
  49. Cai, H.; Xiao, J.; Zhang, Q.; Lian, X. Co-suppressed glutamine synthetase2 gene modifies nitrogen metabolism and plant growth in rice. Chin. Sci. Bull. 2010, 55, 823–833. [Google Scholar] [CrossRef]
  50. Zhang, C.; Lu, W.H.; Yang, Y.; Shen, Z.G.; Ma, J.F.; Zheng, L.Q. OsYSL16 is required for preferential cu distribution to floral organs in rice. Plant Cell Physiol. 2018, 59, 2039–2051. [Google Scholar] [CrossRef]
  51. Yuan, M.; Li, X.; Xiao, J.; Wang, S. Molecular and functional analyses of COPT/Ctr-type copper transporter-like gene family in rice. BMC Plant Biol. 2011, 11, 69. [Google Scholar] [CrossRef]
  52. Yoshida, S.; Forno, D.A.; Cook, J.H.; Gomez, K.A. Laboratory Manual for Physiological Studies of Rice, 3rd ed.; International Rice Research Institute: Manila, Philippines, 1976. [Google Scholar]
Figure 1. Growth phenotype (a), root length (b), plant height (c), and root (d) and shoot (e) dry weight of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Figure 1. Growth phenotype (a), root length (b), plant height (c), and root (d) and shoot (e) dry weight of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Plants 11 02612 g001
Figure 2. N concentration (a) and accumulation (b) in the root, basal node, and shoot of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. The N accumulation was calculated as N concentration × dry weight. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Figure 2. N concentration (a) and accumulation (b) in the root, basal node, and shoot of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. The N accumulation was calculated as N concentration × dry weight. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Plants 11 02612 g002
Figure 3. Root uptake capacity of N (a), N uptake in whole plant (b), root-to-shoot translocation of N (c), and N distribution (d) of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. The N uptake was calculated as the N accumulation of whole plant; the uptake capacity of N was calculated as the N accumulation of whole plant/root dry weight; the root-to-shoot translocation of N was calculated as the N accumulation in shoot/the N accumulation of whole plant; the N distribution in each organ was calculated as the N accumulation in each organ/the N accumulation of whole plant. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Figure 3. Root uptake capacity of N (a), N uptake in whole plant (b), root-to-shoot translocation of N (c), and N distribution (d) of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. The N uptake was calculated as the N accumulation of whole plant; the uptake capacity of N was calculated as the N accumulation of whole plant/root dry weight; the root-to-shoot translocation of N was calculated as the N accumulation in shoot/the N accumulation of whole plant; the N distribution in each organ was calculated as the N accumulation in each organ/the N accumulation of whole plant. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Plants 11 02612 g003
Figure 4. Cu concentration (a) and accumulation (b) in the root, basal node, and shoot of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. The Cu accumulation was calculated as Cu concentration × dry weight. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Figure 4. Cu concentration (a) and accumulation (b) in the root, basal node, and shoot of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. The Cu accumulation was calculated as Cu concentration × dry weight. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Plants 11 02612 g004
Figure 5. Root uptake capacity of Cu (a), Cu uptake in whole plant (b), root-to-shoot translocation of Cu (c), and Cu distribution (d) of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. The Cu uptake was calculated as the Cu accumulation of whole plant; the uptake capacity of Cu was calculated as the Cu accumulation of whole plant/root dry weight; the root-to-shoot translocation of Cu was calculated as the Cu accumulation in shoot/the Cu accumulation of whole plant; the Cu distribution in each organ was calculated as the Cu accumulation in each organ/the Cu accumulation of whole plant. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Figure 5. Root uptake capacity of Cu (a), Cu uptake in whole plant (b), root-to-shoot translocation of Cu (c), and Cu distribution (d) of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM; ++Cu, 1.5 μM) and N (-N, 0.288 mM; +N, 2.88 mM; ++N, 14.4 mM) supply for three weeks. The Cu uptake was calculated as the Cu accumulation of whole plant; the uptake capacity of Cu was calculated as the Cu accumulation of whole plant/root dry weight; the root-to-shoot translocation of Cu was calculated as the Cu accumulation in shoot/the Cu accumulation of whole plant; the Cu distribution in each organ was calculated as the Cu accumulation in each organ/the Cu accumulation of whole plant. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Plants 11 02612 g005
Figure 6. Expression levels of genes involved in NO3 transport (a), NH4+ transport (b), NO3 reduction and NH4+ assimilation (c), and Cu transport (d) in the root and shoots of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM) and N (-N, 0.288 mM; +N, 2.88 mM) supply for three weeks. Data are fold changes of expression levels of N-related genes under +Cu compared to -Cu conditions, or Cu-related genes under +N compared to -N conditions.
Figure 6. Expression levels of genes involved in NO3 transport (a), NH4+ transport (b), NO3 reduction and NH4+ assimilation (c), and Cu transport (d) in the root and shoots of rice plant grown in solutions with different combinations of Cu (-Cu, 0 μM; +Cu, 0.15 μM) and N (-N, 0.288 mM; +N, 2.88 mM) supply for three weeks. Data are fold changes of expression levels of N-related genes under +Cu compared to -Cu conditions, or Cu-related genes under +N compared to -N conditions.
Plants 11 02612 g006
Figure 7. The panicles (a), straw dry weight (b), and grain yield (c) of rice plant grown in soil with different combinations of Cu (-Cu, 0 mg Cu kg−1 soil; +Cu, 50 mg Cu kg−1 soil) and N (-N, 0 g N kg−1 soil; +N, 0.2 g N kg−1 soil; ++N, 0.4 g N kg−1 soil) supply at mature stage. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Figure 7. The panicles (a), straw dry weight (b), and grain yield (c) of rice plant grown in soil with different combinations of Cu (-Cu, 0 mg Cu kg−1 soil; +Cu, 50 mg Cu kg−1 soil) and N (-N, 0 g N kg−1 soil; +N, 0.2 g N kg−1 soil; ++N, 0.4 g N kg−1 soil) supply at mature stage. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Plants 11 02612 g007
Figure 8. The concentration (a), accumulation (b), and distribution (c) of Cu in rice plant grown in soil with different combinations of Cu (-Cu, 0 mg Cu kg−1 soil; +Cu, 50 mg Cu kg−1 soil) and N (-N, 0 g N kg−1 soil; +N, 0.2 g N kg−1 soil; ++N, 0.4 g N kg−1 soil) supply at mature stage. The Cu accumulation was calculated as Cu concentration × dry weight; the Cu distribution in each organ was calculated as the Cu accumulation in each organ/the Cu accumulation of whole plant. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Figure 8. The concentration (a), accumulation (b), and distribution (c) of Cu in rice plant grown in soil with different combinations of Cu (-Cu, 0 mg Cu kg−1 soil; +Cu, 50 mg Cu kg−1 soil) and N (-N, 0 g N kg−1 soil; +N, 0.2 g N kg−1 soil; ++N, 0.4 g N kg−1 soil) supply at mature stage. The Cu accumulation was calculated as Cu concentration × dry weight; the Cu distribution in each organ was calculated as the Cu accumulation in each organ/the Cu accumulation of whole plant. Data are means ± SD of three biological replicates. Different letters indicate significant difference at p < 0.05 by Tukey’s test.
Plants 11 02612 g008
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Cui, X.; He, H.; Hu, S.; Zhang, B.; Cai, H. Synergistic Interaction between Copper and Nitrogen-Uptake, Translocation, and Distribution in Rice Plant. Plants 2022, 11, 2612. https://doi.org/10.3390/plants11192612

AMA Style

Cui X, He H, Hu S, Zhang B, Cai H. Synergistic Interaction between Copper and Nitrogen-Uptake, Translocation, and Distribution in Rice Plant. Plants. 2022; 11(19):2612. https://doi.org/10.3390/plants11192612

Chicago/Turabian Style

Cui, Xinlong, Hua He, Shengwang Hu, Banfa Zhang, and Hongmei Cai. 2022. "Synergistic Interaction between Copper and Nitrogen-Uptake, Translocation, and Distribution in Rice Plant" Plants 11, no. 19: 2612. https://doi.org/10.3390/plants11192612

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop