- 1Council of Scientific & Industrial Research (CSIR)-Indian Institute of Integrative Medicine, Jammu, India
- 2Academy of Scientific and Innovative Research, Ghaziabad, India
- 3Department of Botanical and Environmental Sciences, Guru Nanak Dev University, Amritsar, India
Salt stress adversely influences growth, development, and productivity in plants, resulting in a limitation on agriculture production worldwide. Therefore, this study aimed to investigate the effect of four different salts, i.e., NaCl, KCl, MgSO4, and CaCl2, applied at various concentrations of 0, 12.5, 25, 50, and 100 mM on the physico-chemical properties and essential oil composition of M. longifolia. After 45 days of transplantation, the plants were irrigated at different salinities at 4-day intervals for 60 days. The resulting data revealed a significant reduction in plant height, number of branches, biomass, chlorophyll content, and relative water content with rising concentrations of NaCl, KCl, and CaCl2. However, MgSO4 poses fewer toxic effects than other salts. Proline concentration, electrolyte leakage, and DPPH inhibition (%) increase with increasing salt concentrations. At lower-level salt conditions, we had a higher essential oil yield, and GC–MS analysis reported 36 compounds in which (−)-carvone and D-limonene covered the most area by 22%–50% and 45%–74%, respectively. The expression analyzed by qRT-PCR of synthetic Limonene (LS) and Carvone (ISPD) synthetic genes has synergistic and antagonistic relationships in response to salt treatments. To conclude, it can be said that lower levels of salt enhanced the production of essential oil in M. longifolia, which may provide future benefits commercially and medicinally. In addition to this, salt stress also resulted in the emergence of novel compounds in essential oils, for which future strategies are needed to identify the importance of these compounds in M. longifolia.
1 Introduction
Under varying environmental conditions, plants are exposed to different stresses. There are many inbuilt mechanisms in plants by which they respond to these abiotic as well as biotic stresses, such as by altering the expression levels of several genes, cellular metabolism, growth rate, and morphology (Iqbal et al., 2021). In the framework of agronomy, these stress factors cause significant deviations in crop production. Among all stresses, salinity is known to be one of the most detrimental to crop growth and production (Kalefetoğlu and Ekmekci, 2005). In general, salinity is divided into primary and secondary salinities. A primary salinity is the result of natural processes such as weathering, rainfall, and strong winds that deposit salts over time on land and in water. Anthropogenic activities such as deforestation, land clearing, and excessive irrigation contribute to secondary salinity (Arif et al., 2020).
About one billion hectares of land surface area are altered by salinity, which approximates 7% of the entire land surface globally (Ghassemi et al., 1995; Qadir et al., 2014; Negacz et al., 2022). Although most of it is caused by natural geochemical progressions, it is estimated that 30% of irrigated land worldwide is contaminated by secondary salinization via anthropogenic activities (Machado and Serralheiro, 2017; Shahid et al., 2018; Hopmans et al., 2021). In a salinity-rich environment, higher ion concentration creates an osmotic imbalance, due to which water uptake in plants is negatively impacted (Khare et al., 2020; Ali et al., 2021; Ivy et al., 2022). It also reduces chlorophyll content, damages chloroplast ultrastructure, and reduces stomatal conductance, which hampers photosynthetic machinery, transpiration, and gas exchange (Arif et al., 2020; Thorne et al., 2020; El Sabagh et al., 2021).
Salinity stress changes the patterns of accumulation of secondary metabolites in plants (Gengmao et al., 2014; Yang and Guo, 2018). In Rauvolfia tetraphylla and Catharanthus roseus, the content of reserpine and vincristine alkaloids shows enhancement when subjected to salt stress, and it similarly enhances the essential oil (EO) content in Salvia officinalis, Satureja hortensis, and Matricaria recutita (Ashraf et al., 2018). Aromatic plants also accumulate secondary metabolites, including essential oil components, in response to salinity stress (Miransari et al., 2021).
As far as the soil salinity is concerned, sodium chloride (NaCl) and other salts like calcium chloride (CaCl2), magnesium chloride (MgCl2), sodium sulfate (Na2SO4), magnesium sulfate (MgSO4), sodium nitrate (Na2NO3), potassium nitrate (KNO3), etc. are also known to affect plant growth and development (Narjary et al., 2017). Soil salinity can be reversed, but it is time-consuming and relatively expensive. However, the plantation of salinity-resistant crops could be an effective and successful practice in such areas (Kulak et al., 2020).
M. longifolia (L.) Hudson is an important medicinal plant of the Lamiaceae (syn. Labiatae). It is a rapid-growing perennial aromatic herb with creeping rhizomes, commonly called ‘wild mint’ or ‘horse mint’ (Araghi et al., 2019; Moetamedipoor et al., 2021). It is widely distributed across Asia, Africa, Europe, Australia, and North America (Segev et al., 2012). M. longifolia is extensively used for its herbage and essential oils (Kumar et al., 2015; Jedrzejczyk and Rewers, 2018; Soilhi et al., 2019). Several pharmaceutical activities of both essential oils and extracts of M. longifolia have been investigated, including antimicrobial, antispasmodic, anticancer, antioxidant, hypertension, heart diseases, and most importantly, lowering the risk of cancer (Valko et al., 2006; Razavi et al., 2012; Hintz et al., 2015; Patonay et al., 2019). It also helps boost the immune system and fight secondary infections (Okut et al., 2017).
In the traditional systems of medicine all over the world, M. longifolia has been used for the treatment of gastrointestinal disorders, inflammatory disorders, respiratory diseases, infectious diseases, and menstrual disorders (Farzaei et al., 2017a). It is also used for the treatment of throat and mouth irritation (Farzaei et al., 2017b). In several food products like chewing gum, ice cream, candies, beverages, and non-vegetarian food items, the fresh leaves of M. longifolia are used as condiments (Krzyzanowska et al., 2011).
In saline areas, the selection of plants with salt tolerance is of great importance for bringing these areas into agricultural production. Higher economic value and desired chemical content are important targets in the selection of plants to be grown in these areas. However, studies regarding the physiological, biochemical, and molecular aspects of M. longifolia under different salt stress conditions are still lacking. A few investigations have been done on related phytochemical changes and secondary metabolites in M. longifolia grown under salinity conditions (El-Alakmy et al., 2017). The present study aimed to investigate the physiological, biochemical, molecular, and oil content of M. longifolia treated with NaCl, KCl, MgSO4, and CaCl2 at different concentrations (12.5, 25, 50, and 100 mM), whereas non-treated control plants were taken for comparison. Furthermore, the expression patterns of genes associated with the biosynthesis of mint essential oil were also analyzed at different salinity concentrations, and gene expression was correlated with the oil content.
2 Material and methods
2.1 Plant material
M. longifolia plant material was taken from the Chatha farm at CSIR-IIIM, Jammu. An herbarium specimen of M. longifolia was submitted to the Janaki Ammal Herbarium of the CSIR-Indian Institute of Integrative Medicine, Jammu, J&K, under voucher number 26772 after being morphologically identified by the plant taxonomist using taxonomical guidelines.
2.2 Pot preparation and treatments
The experiments were conducted in the greenhouse of the CSIR-Indian Institute of Integrative Medicine (CSIR-IIIM), located at an altitude of 327 m at 32.7315° N and 74.8505° E, from February to July 2021. The average monthly maximum and minimum temperature, relative humidity, and precipitation were recorded and are shown in Figure 1 (data acquired from a weather station at the agronomy division of Sher-e-Kashmir University of Agricultural Sciences and Technology, Jammu). A 3:1 ratio of soil and manure was used to fill the pots (5 kg). Physical and chemical properties such as pH, electrical conductivity (EC), percentage of clay, sand, and silt, percentage of organic carbon, available nitrogen, available phosphorous, and available potassium (NPK) content were analyzed (Table 1) by methods described in our previous work (Singh et al., 2022). Water holding capacity (WHC) of soil was determined by the cup method as described by George et al. (2013). Four suckers of uniform maturity level and full-grown M. longifolia were planted in a plastic pot containing a soil mixture. Pots were kept in a greenhouse until a growing node appeared. Every treatment was given in three replicates (three different pots; one per replicate), and each pot had four plants. Plants were irrigated twice a week for two months after one month of transplantation to induce salt stress. In the experiment, four salts—NaCl, KCl, MgSO4, and CaCl2—were dissolved in water at four different concentrations: 12, 25, 50, and 100 mM, and an untreated control was also used.
Figure 1 Meteorological data on maximum and minimum temperature (°C), maximum and minimum relative humidity (%) and total rainfall (in) during the experiment (from plant transplantation to harvesting). TM, temperature; RH, relative humidity; RF, rainfall.
2.3 Morphological parameters
After 15 d of salt treatment, when the plants were at the flowering stage, the plant height was measured and the number of branches of M. longifolia in each pot was counted (Figure 2). The plants were then harvested, and the roots and shoots of each treatment were separated. Both the root and shoot were washed twice with tap water, followed by distilled water. The fresh weight of the treated and control plants was taken using a weighing balance (Intwel, JW 24459). The plants were dried in an oven at 80°C for 48 h to achieve a constant dry weight before dry weight measurements.
Figure 2 Morphology of M. longifolia plants (A—shoot and B—root) treated with salts. (1) NaCl, (2) KCl, (3) MgSO4, and (4) CaCl2.
2.4 Analyses of relative water content and electrolyte leakage
M. longifolia leaves of similar maturity levels were collected 24 h after salt treatment for relative water content (RWC) and electrolyte leakage (EL) analyses. The fresh weight of each leaf was taken before soaking the leaves in distilled water in sealed test tubes overnight at room temperature, after which the turgid weight was measured. The soaked leaves were dried in an oven for 24 h at 80°C when the weight was constant, and their dry weight was calculated. RWC was calculated using the formula given by Henson et al. (1981) and El-Bassiouny and Bekheta (2005).
EL was determined by adopting the method of Dionisio-Sese and Tobita (1998). Briefly, 0.5 g of fresh leaves were chopped into small pieces (10 mm) and transferred to 20 ml of double-distilled water (ddH2O). The test tubes were incubated at 32°C in a water bath for 2 h. After the tubes had cooled down, the electrical conductivity (EC1) of the supernatant was determined using a conductivity meter (VSI-04ATC, VSI Electronics, India). After this, the samples were autoclaved for 20 min at 121°C, cooled to 25°C, and EC2 was determined. Then the electrolyte leakage was calculated using the following formula:
2.5 Measurement of chlorophyll content
Photosynthetic pigments such as chlorophyll a (chl a), chlorophyll b (chl b), chlorophyll ab (chla + b), and carotenoids were measured by following the methods of Lichtenthaler (1987) and Voko et al. (2022). In 5 ml of ice-cold acetone, 0.10 g of fresh leaf tissue of similar maturity level was ground using a pestle and mortar. Then the extract obtained was filtered through filter paper (Whatman, GE Healthcare, UK), and an UV-visible spectrophotometer (Eppendorf, Biospectrophotometer, Eppendorf AG, 22331 Hamburg) was used to measure the absorbance at 470, 645, and 662 nm. The values obtained from the spectrophotometer were then calculated as described by Lichtenthaler (1987) for chl a, chl b, ch la + b, and carotenoids
2.6 Estimation of proline content
Fresh leaves of M. longifolia were taken for determination of proline content as described by Bates et al. (1973) with minor modifications. Briefly, 0.5 g of fresh leaves were homogenized with 10 ml of 3% sulfosalicylic acid. The homogenate obtained was filtered, then 1 ml of ninhydrin and 1 ml of glacial acetic acid were added, and the mixture was left undisturbed for an hour in a water bath set at 100°C. After incubation, it was cooled; the mixture was extracted with toluene, and the absorbance was measured at 520 nm. L-proline was used as a reference.
2.7 Estimation of DPPH inhibition percentage
Using the protocol described by Brand-Williams et al. (1995) and Xiao et al. (2020), the DPPH (1, 1-diphenyl-2-picryl-hydrazil) assay was carried out. The DPPH solution was prepared by dissolving 7.89 mg of DPPH in 100 ml of 99.50% ethanol and keeping it in the dark for 2 h. An ethanolic solution of ascorbic acid (1 mg/ml) was used as the standard. Approximately 200 µl of the extract was mixed with 1,000 µl of DPPH solution and 800 µl of the Tris–HCL buffer (pH 7.4), and the solution was kept for 30 min at room temperature (RT). The absorbance was then taken at 517 nm. Approximately 1,200 µl of ethanol and 800 µl of Tris–HCL buffer (pH 7.4) were mixed. Approximately 200 µl of this ethanol–Tris–HCL mix was used instead of a sample for measurement. The DPPH inhibition % was calculated with the following formula:
2.8 Essential oil extraction
Hydro-distillation of fresh plant materials (100 g) was carried out for 3 h in a Clevenger (500 ml) along with water (200 ml). A pooled sample from each replicate was hydrodistilled. The essential oil was obtained after 3 h, dehydrated with anhydrous sodium sulfate salt, and stored in a refrigerator at 4°C.
2.9 Analysis of essential oil using gas chromatography and mass spectrometry (GC–MS)
Agilent 7890A gas chromatography linked to a 5875C mass spectrometer detector (XL MSD) with triple axis and MassHunter workstation software (USA) was used to analyze the samples. The column (Agilent) used was DB-5: 30 m × 0.25 mm i.d. × 0.25 μm film thickness. Helium operates as a carrier gas at a flow rate of 0.50 ml/min. The oven temperature of the gas chromatography was increased at a rate of 10°C/min from 200°C for 2 min to 280°C for 20 min. Approximately 1 μl of injection volume was done with a split ratio of 1:50. The mass spectra were captured in electron impact mode across the range of 50–600 amu at a scan rate of 0.5 s/scan and an ionization energy of 70 eV. The inlet and transfer line temperatures were maintained at 250°C. Wiley and NIST libraries were used for identifying components. Peak area percentages were electronically estimated without the use of correction factors from the TIC response.
2.10 Total RNA isolation, DNase treatment, and cDNA synthesis
TRIzol reagent (Ambion, Life Technologies, Carlsbad, USA) was used to isolate total RNA from M. longifolia leaves exposed to different salt concentrations following the manufacturer’s instructions. The integrity of isolated RNA was checked by 2% agarose gel electrophoresis. The NanoDrop Spectrophotometer (Thermo Fisher Scientific, Waltham, Massachusetts, USA) was used to analyze the absorbance ratio at 260/280 nm to determine the purity and concentration of total RNA. To remove any remaining genomic DNA contamination, the RNA samples were treated with DNase (Ambion TURBO DNA-free, Life Technologies, Carlsbad, CA, USA). A negative control PCR was carried out using the primers of the housekeeping gene to check for any potential DNA contamination in the DNase-treated RNA samples. cDNA was prepared from the DNase-treated RNA using a cDNA synthesis kit (Promega, Madison, WI, USA) in accordance with the manufacturer’s instructions. DNase-treated RNA samples were reverse-transcribed using a reverse transcriptase enzyme, oligo (dT) primers and 1 µg of DNase-treated RNA as a template.
2.11 qRT-PCR
Primer pairs (Table 2) were designed using the coding sequences (CDS) of the carvone and limonene biosynthesis genes of M. longifolia. The qRT-PCR experiments were carried out using the SYBR green master mix and the CFX96TM RT-PCR Detection System (Bio-Rad in Hercules, California, USA). The PCR reaction mixtures (10 μl) contained SYBR Green Master Mix 5.0 μl, Primer 1.0 µM (Saha Gene, Hyderabad, Telangana, India), appropriately diluted cDNA as a template, and the final volume of 10 μl was made up of MQ water. The thermoprofiles of the qRT-PCR reactions were included by preincubating at 95°C for 10 min, followed by 45 cycles of 3-step amplification (95°C for 10 s, 55°C for 10 s, and 72°C for 15 s) and melting. The reaction was normalized by using the primers for the 5.8 s gene as a reference. The fold change was then calculated using the 2−ΔΔCT approach utilizing the threshold cycle (CT) (Ahmed et al., 2022).
2.12 Statistical analysis
Each treatment was carried out in three replicates, and the data were represented as means. A one-way analysis of variance (ANOVA) was used to statistically evaluate the data using Excel 2019 and IBM SPSS Statistics version 26. The significant group was analyzed via Duncan’s multiple range analysis. Student t-tests were performed for a significant difference in the relative fold change of selected genes. Furthermore, the variances between the specific means were considered significant at p <0.05. PAST software and Origin Pro 2021 software were used to create the principal component analysis and correlation map, respectively.
3 Results
3.1 Morphology
The results showed that in M. longifolia, all four salts (NaCl, KCl, MgSO4, and CaCl2) led to significant changes in plant height (F = 3.17; p = 0.00), number of branches (F = 4.431; p = 0.00), number of inflorescences (F = 2.71; p = 0.01), plant fresh weight (F = 50.81; p = 0.00), and plant dry weight (F = 122.22; p = 0.00) (Table 3). In this case, F represents the variance of group mean values, and P represents the probability. All four (12.5, 25, 50, and 100 mM) concentrations of NaCl significantly reduced plant height by 16%, 12%, 21%, and 20%, respectively. With KCl treatments (12.5, 25, and 100 mM), the plant height was decreased by 7%, 2%, and 6%, whereas with 50 mM of KCl, a slight increase in height (2%) was observed when compared with the control. A 25 and 50 mM concentration of MgSO4 showed a 5% improvement in plant height. CaCl2 treatments (50 and 100 mM) resulted in a reduction in plant height of 6% and 13%, respectively. All salts significantly affected the number of branches. Maximum reduction (40%) occurred in 100 mM NaCl, followed by 19% in the CaCl2, and 14% in the KCl treatment. The number of branches improved (19%) with a 50 mM MgSO4 concentration. However, a 3% reduction in the number of branches was noticed at 100 mM MgSO4 concentration. As a result of salt stress, inflorescences significantly decreased. In comparison with the control group, 100 mM of KCl showed the highest reduction (52%), and 25 mM of MgSO4 showed the lowest reduction (8%) in the number of branches. Similarly, under salinity stress, the biomass (dry weight) of plants was also significantly reduced. Compared to the control, increasing NaCl concentrations reduced the total biomass of M. longifolia by 33%, 32%, 41%, and 58%, respectively. Similarly, plants treated with KCl showed reductions in total biomass of 47%, 53%, 59%, and 74% as compared to the control. In the case of CaCl2, too, a marked reduction in biomass occurred (59%, 57%, 45%, and 53%) with increasing salt concentrations. However, the effect of MgSO4 on total plant biomass was relatively subdued in comparison to NaCl, KCl, and CaCl2. Increased concentrations (12.5, 25, 50, and 100 mM) of MgSO4 reduced the biomass of M. longifolia by 34%, 15%, 50%, and 28%, respectively. In comparison with the control groups, all salts showed a deleterious effect on biomass, but a linear relationship between biomass and change in concentration was not observed. Here, the highest biomass was noted with a 25 mM MgSO4 treatment close to the control group, whereas the lowest biomass was noted with a 100 mM KCl treatment.
3.2 Relative water content of leaves and electrolyte leakage
RWC of leaves was significantly affected by all four salt conditions: NaCl (F = 4.73; p = 0.02), KCl (F = 5.83; p = 0.01), MgSO4 (F = 4.51; p = 0.02), and CaCl2 (F = 4.58; p = 0.02). RWC significantly decreased with increasing salt concentrations (Figure 3). RWC was found to be highest in the control group (72.19%) and lowest in the 100 mM NaCl group (31.81%). NaCl, KCl, and CaCl2 affected RWC to a greater extent as compared with MgSO4, which was found to be less harmful.
Figure 3 Effect of 12.5, 25, 50, and 100 mM concentrations of NaCl, KCl, MgSO4, and CaCl2 salts on leaf relative water content (%) in an M. longifolia leaf sample. The data are represented as mean ± standard deviation (n = 3). The different letters on the bar graph show the significantly different groups according to the Duncan test (α = 0.05).
An El test demonstrates the leaf sample’s membrane stability (Henson et al., 1981). El increased significantly with increasing salt concentrations, as shown in Figure 4. On average, in M. longifolia leaves treated with various concentrations of different salts, the highest El was observed in CaCl2 (89.04%), followed by KCl (88.21%), NaCl (87.17%), and MgSO4 (82.10%). Plants in the control group had the lowest El (68.16%). Among the treatments with different concentrations of NaCl, El was highest at 12.5 mM and decreased with increasing NaCl concentrations. With KCl, El increased up to 50 mM of salt concentration, while it slightly decreased at 100 mM of concentration. Although, on treatment with MgSO4 and CaCl2, EI significantly increased with increasing salt concentrations.
Figure 4 Effect of 12.5, 25, 50, and 100 mM concentrations of NaCl, KCl, MgSO4, and CaCl2 salts on electrolyte leakage (%) in an M. longifolia leaf sample. The data are represented as mean ± standard deviation (n = 3). The different letters on the bar graph show the significantly different groups according to the Duncan test (α = 0.05).
3.3 Photosynthetic pigments
In M. longifolia plants treated with different concentrations of salts, the levels of photosynthetic pigments were significantly decreased with an increasing salt concentration in the soil when compared to the control. The maximum reduction in pigments was noticed in all salt treatments at 100 mM concentration. The NaCl treatment showed the most detrimental effect on the content of pigments: chl a, chl b, chl a + b, and carotenoid (1.58, 0.84, 2.43, and 1.96 mg g−1) in comparison with the control plant (9.30, 4.58, 13.89, and 5.86 mg g−1), respectively (Figure 5). After NaCl, KCl showed the maximum reduction in pigment at 100 mM concentration. In KCl treatment, chl a was reduced from 9.39 mg g−1 (12.5 mM) to 1.58 mg g−1 (100 mM); chl b from 4.70 mg g−1 (12.5 mM) to 1.51 mg g−1 (100 mM); and chl a + b from 14.11 mg g−1 (12.5 mM) to 3.04 mg g−1 (100 mM) (Figure 5). The MgSO4 treatment resulted in the least negative effect on pigment content compared to other salt treatments (Figure 5).
Figure 5 1. Chlorophyll content and total carotenoid content (mg g−1) in an M. longifolia leaf sample under salt stress condition. (A) Different concentrations of NaCl; (B) Different concentrations of KCl; (C) Different concentrations of MgSO4; and (D) Different concentrations of CaCl2. The data are represented as mean ± standard deviation (n = 3). The different letters on the same color bar show the significantly different groups according to the Duncan test (α = 0.05). 2. Photosynthetic pigment in an M. longifolia leaf sample under different salt stress conditions.
3.4 Proline content
In our experiments, the proline content in M. longifolia ranged between 1.40 µg g−1 (control) and 4.28 µg g−1 (100 mM NaCl). NaCl, MgSO4, and CaCl2 all had a significant effect on proline content (F = 26.62; p = 0.00), (F = 216.22; p = 0.00), and (F = 60.37; p = 0.00), respectively. While KCl treatment did not significantly (F = 6.13; p = 0.09) affect proline content. According to observations, the proline content increased with increasing salt concentration (Figure 6). When compared to all salt treatments, NaCl showed variability in proline content. Approximately 12.5 mM NaCl showed the lowest proline content (1.54 µg g−1) followed by 100 mM NaCl, which showed the highest proline content (4.28 µg g−1). In plants treated with 12.5 mM and 50 mM of KCl, the proline content was increased by 2.34 and 2.193 µg g−1), and moderately decreased when treated with 25 mM and 100 mM (2.06 and 1.89 µg g−1, respectively). The MgSO4 salt stress showed an increase in proline content (2.023 µg g−1) up to 50 mM and then slightly decreased (2.003 µg g−1) at 100 mM concentration.
Figure 6 Effect of 12.5, 25, 50, and 100 mM concentrations of NaCl, KCl, MgSO4, and CaCl2 salts on proline content (µg g−1 fresh weight) in an M. longifolia leaf sample. The data are represented as mean ± standard deviation (n = 3). The different letters on the same color bar show the significantly different groups according to the Duncan test (α = 0.05).
3.5 DPPH inhibition
KCl (F = 4.01; p = 0.03), MgSO4 (F = 4.79; p = 0.02), and CaCl2 (F = 8.28; p = 0.003) significantly affected the DPPH inhibition percentage. While NaCl salt treatment did not significantly (F = 2.31; p = 0.12) affect DPPH activity. DPPH inhibition in M. longifolia increased with increasing salt concentrations (Figure 7). At 100 mM salt concentrations, CaCl2 treatment resulted in the highest scavenging activity (70.26%), followed by KCl (69.80%), and NaCl (68.09%), whereas MgSO4-treated plants showed the least activity (67.63%). Instead of 12.5 mM CaCl2, all salt treatments led to an increase in scavenging activity as compared to the control group.
Figure 7 Effect of 12.5, 25, 50, and 100 mM concentrations of NaCl, KCl, MgSO4, and CaCl2 salts on DPPH inhibition % (antioxidant activity) in an M. longifolia leaf sample. The data are represented as mean ± standard deviation (n = 3). The different letters on the same color bar show the significantly different groups according to the Duncan test (α = 0.05).
3.6 Essential oil yield
The essential oil yield of M. longifolia ranges from 0.357 ml (100 mM KCl) to 0.727 ml (12.5 mM MgSO4) in 100 g of fresh plant sample (Figure 8). Different concentrations of MgSO4 showed a positive effect on oil yield (27.27%, 26.00%, 23.95%, and 16.66%), respectively, compared to the control. Approximately 12.5 mM concentrations of NaCl and KCl caused an increment in oil yield of 3.42% and 14.65%, respectively, while the yield was decreased when NaCl and KCl concentrations were increased. In samples treated with 12.5, 25, and 50 mM of CaCl2, the oil yield was found to be increased by 0.71%, 4.05%, and 3.90%, respectively, compared to the control group.
Figure 8 Effect of 12.5, 25, 50, and 100 mM concentrations of NaCl, KCl, MgSO4, and CaCl2 salts on essential oil yield in an M. longifolia leaf sample.
3.7 Components of essential oil
A gas chromatography–mass spectrometry (GC–MS) study of the composition of essential oils is provided in Tables 4–7. Salt stress significantly affected all the components identified in the oil of M. longifolia. The two main constituents of essential oils were (−)-carvone and D-limonene. These two components occupied 96% of the essential oils. The chromatogram and mass spectra of (−)-carvone and D-limonene from the control sample are shown in Figure 9. The samples treated with 50 mM CaCl2 showed the highest concentration of carvone (7.58%), which is higher than that of 100 mM CaCl2 (4.67%) as compared to the control. A negative relationship exists between the accumulation percentages of limonene and carvone in our experiments. Salt treatments such as NaCl and KCl (100 mM), MgSO4 (50 mM and 100 mM), and CaCl2 (12.5 mM) decreased the accumulation of carvone, whereas a significant increase in limonene content was seen at the above-mentioned concentrations (18.98%, 1.16%, 13.51%, 24.70%, 6.10%, and 0.86%, respectively) (Figures 10, 11).
Table 4 Composition of essential oil under different NaCl salt concentration treatments of M. longifolia fresh plant material.
Table 5 Composition of essential oil under different KCl salt concentration treatments of M. longifolia fresh plant material.
Table 6 Composition of essential oil under different MgSO4 salt concentration treatments of M. longifolia fresh plant material.
Table 7 Composition of essential oil under different CaCl2 salt concentration treatments of M. longifolia fresh plant material.
Figure 9 GC–MS chromatograms of the dominant compounds (A) limonene and (B) carvone of essential oil in M. longifolia.
Figure 10 Limonene % area obtained from GC–MS analysis in an M. longifolia essential oil sample under salt stress condition. (A) Different concentrations of NaCl; (B) Different concentrations of KCl; (C) Different concentrations of MgSO4; and (D) Different concentrations of CaCl2. The data are represented as mean ± standard deviation (n = 3).
Figure 11 Carvone % area obtained from GC–MS analysis in an M. longifolia essential oil sample under salt stress condition. (A) Different concentrations of NaCl; (B) Different concentrations of KCl; (C) Different concentrations of MgSO4; and (D) Different concentrations of CaCl2. The data are represented as mean ± standard deviation (n = 3).
Other components obtained from the essential oil of M. longifolia with more than 0.2% in the control plant group were alpha-pinene (0.20%), beta-pinene (0.23%), eucalyptol (0.35%), cyclohexanone, 2-methyl-5-1-methylethenyl (1.62%), and caryophyllene (0.26%) (Tables 4-7).
3.8 Correlation analysis and principal component (PCA) analysis
The Pearson correlation was plotted among different plants’ physiological and biochemical parameters, such as photosynthetic pigment, El, RWC, proline content, DPPH inhibition %, carvone, and limonene %, with different salt stress treatments in M. longifolia (Figure 12). According to the observation, the percentages of photosynthetic pigment, RWC, and carvone were negatively correlated with the percentages of El, proline content, DPPH inhibition, and limonene. However, the pigments have a strong positive correlation with each other, represented by brown color, and show a high correlation coefficient (r) value (r = 0.73 to r = 0.97). Moreover, the carvone and limonene percentages show a strong negative correlation (r = −1), represented by the purple color.
Figure 12 Correlation among chlorophyll (a), chlorophyll (b), chlorophyll (a + b), total carotenoids, leaf relative water content, electrolyte leakage, proline content, DPPH inhibition %, carvone and limonene % area. The brown color boxes show a strong correlation, and the purple color boxes show a weak correlation.
The physico-chemical parameters such as photosynthetic pigments, El, RWC, proline content, DPPH inhibition percentage, carvone, and limonene percentage were subjected to principal component analysis (Figure 13). The biplot (score and loading) from PCA displayed that the first two PCs exhibited overall variability of 84.50%. However, the second and third PCs showed overall variability of 97.48%. The PC1 independently has 56.50% variance, and the PC2 independently has 28.0% variance. The pigments and percentage of carvone have a positive association with PC1 and PC2. The El and DPPH percentage inhibition have a positive association with PC1 and a negative association with PC2, whereas the proline content and limonene percentage have a negative association with PC1 and PC2.
Figure 13 Principal component analysis (PCA) biplots of M. longifolia chlorophyll (a), chlorophyll (b), chlorophyll (a + b), total carotenoids, leaf relative water content, electrolyte leakage, proline content, DPPH inhibition %, carvone and limonene % area with different (12.5, 25, 50, and 100 mM) concentrations of NaCl, KCl, MgSO4, and CaCl2 salts compared to the control plant.
3.9 Expression analysis of key genes involved in carvone and limonene biosynthesis
Geranyl pyrophosphate synthase (GPPS), Limonene-6-hydroxylase (L-6-H), Limonene synthase (LS), and Isopiperitenol dehydrogenase (ISPD) are the key genes involved in the carvone and limonene biosynthetic pathways. Their expression was examined at the transcript level in samples treated with different concentrations of NaCl, KCl, MgSO4, and CaCl2 (Figure 14). These genes showed significant changes in their expression patterns in treated plants compared to the control group of M. longifolia. As compared to control, the expression of GPPS and L-6-H was increased by 1.30 and 1.12 folds with 12.5 mM NaCl treatment, respectively, and decreased (1.13, 0.81, and 0.18 folds, respectively) with 25, 50, and 100 mM NaCl treatment. With 12.5, 25, and 50 mM NaCl treatment, LS gene expression decreased by 0.09, 0.64, and 0.55-fold, and slightly increased by 0.65-fold with 100 mM NaCl but did not exceed control levels. At 50 mM NaCl treatment, there was no significant variation in the expression of the ISPD gene. But it significantly decreased with 100 mM NaCl treatment compared to control.
Figure 14 qRT-PCR-based expression analysis of key genes of the carvone and limonene biosynthesis pathways of M. longifolia. The bar diagrams represent the fold change in expression of each gene upon 12.5, 25, 50, and 100 mM salt treatment as compared to untreated controls. (A–D) Different concentrations of NaCl; (E–H) Different concentrations of KCl; (I–L) Different concentrations of MgSO4; and (M–P) Different concentrations of CaCl2. The results are presented as the means of three replicates and as means ± SDs. Statistical significance was determined by the Student’s t-test. Letters a and b denote the significance of fold changes at p-values <0.05 (a <0.005, b<0.05) while letter c denotes the non-significant nature of fold changes at p-values >0.05.
GPPS expression was not significantly altered with 12.5 mM of KCl concentration, but was significantly decreased (0.34, 0.43, and 0.74 folds) with 25, 50, and 100 mM KCl concentrations, respectively, when compared with control. Moreover, the expression level of the L-6-H gene was found to be significantly increased by 14.50-fold in plants exposed to 25 mM of KCl and then further decreased (11.28 and 2.41-fold) with 50 mM and 100 mM of KCl, but not less than control. With 25 and 50 mM of KCl treatment, the expression of the LS gene did not significantly change, but with 50 and 100 mM of KCl, it increased substantially by 2.22 and 41.70-fold, respectively. 12.5, 25, and 50 mM KCl treatments did not significantly affect the expression of the ISPD gene, while 100 mM KCl treatments significantly decreased it compared with the control.
On exposure to 12.5, 25, and 50 mM MgSO4, the expression of the GPPS and L-6-H genes decreased by 0.01, 0.04, 0.21-fold, and 0.10, 0.20, and 0.60-fold, respectively, and increased by 1.04-fold and 1.3-fold with 100 mM MgSO4 treatment. Similarly, MgSO4 at 12.5 and 25 mM decreased the transcripts of the LS gene. In comparison to the control plant group, the transcript level of ISPD increased at all concentrations of MgSO4. As compared with the control, the CaCl2 salt increased the transcription levels of the GPPS and L-6-H genes. Furthermore, the LS gene expression slightly decreased at 12.5 mM CaCl2, and no significant difference was observed at 25 and 100 mM CaCl2 concentrations. However, the expression of the ISPD gene increased by 6.19, 5.80, 5.47, and 6.82-folds with increasing concentrations of CaCl2 salt when compared to control.
4 Discussion
Salinity inhibits plant growth by causing osmotic stress, ionic imbalance, and nutritional imbalance (Khare et al., 2020; Ali et al., 2021; Ivy et al., 2022). Such deficits have a negative impact on plant growth and development (Shrivastava and Kumar, 2015). The current study was aimed at investigating the morphological, physiological, and biochemical status of M. longifolia exposed to four different types of salts (NaCl, CaCl2, KCl, and MgSO4) at four different concentrations (12.5, 25, 50, and 100 mM) in soil. The salt stress showed a detrimental effect on plant physiological and morphological parameters. The results revealed that NaCl, CaCl2, and KCl salt showed harmful effects at over 50 mM concentrations in M. longifolia. NaCl and KCl have the most toxic effects at higher concentrations than CaCl2 and MgSO4. Similarly, Kulak et al. (2020) also noted that NaCl and KCl are more detrimental than CaCl2 and MgSO4 to S. officinalis. Interestingly, among these salts, 12.5 mM, and 25 mM of MgSO4 have a beneficial effect on plant height. However, the biomass was found to be reduced in plants that grew at all concentrations of MgSO4.
The effects of salinity caused by NaCl on plant physiology are common (Fageria et al., 2012). The previous study also shows that increased concentrations of NaCl have an adverse effect on morphology in other plants, such as Dracocephalum moldavia L. (Mohammadi et al., 2021), Ocimum basilicum L. (Lazarević et al., 2021), Oenanthe javanica (Kumar et al., 2021), Suaeda salsa (Zhang et al., 2020), Glycine max L. (Jabeen et al., 2021), Hordeum vulgare, Lactuca sativa, and Helianthus annuus (Szymańska et al., 2022). High Na+ interferes with the allocation of other important minerals and reduces water uptake; it alters membrane lipids and induces ROS generation, leading to lipid peroxidation, resulting in a decrease in RWC, photosynthetic pigments, and an increase in El, proline content, DPPH activity in M. longifolia. High Na+ levels can depolarize and injure the plasma membrane, limiting K+ uptake and leaking; additionally, Na+ can replace K+ in key enzymatic reactions, further compromising cellular functions in the cytosol and organelles (Almeida et al., 2017; Cirillo et al., 2019). A similar study was also documented in Dracoceplalum kotschyi, where the increasing NaCl (25, 50, 75, and 100 mM) concentration decreased the RWC and photosynthetic pigments had increased El and proline content (Vafadar et al., 2020). In Thymus vulgaris and Thymus daenensis, the application of NaCl stress reduced the chlorophyll content and seedling growth and increased the El (Bistgani et al., 2019). In O. basilicum, the membrane permeability, essential oil content, and proline content were increased with NaCl salt stress (Farsaraei et al., 2020). Salt stress lowers the rate of photosynthesis. This might also be a direct result of the salt-induced leaf lamina width reduction; in fact, the area-based photosynthetic capacity is directly related to leaf width (Wyka et al., 2012). Osmotic stress can also adversely affect the activities of stomatal enzymes and the closure of stomata, which in turn results in CO2 reduction. Salt stress also inhibits the electron transport chain and results in the inactivation of photosystem II reaction centers. It also destroys the oxygen evolution complex (OEC) and impairs the electron transfer capacity on the donor side of PSII. Increased levels of sodium ions in the non-stomatal leaf tissues can also significantly affect the metabolic processes that limit photosynthesis. Houimli et al. (2010) reported that NaCl stress has more effects on chlorophyll b than chlorophyll a. This increase in the chlorophyll a/chlorophyll b ratio in NaCl exposure is because of the first step of chlorophyll b degradation that results in its conversion into chlorophyll a, and therefore, a decrease in total chlorophyll content (Gomes et al., 2017).
KCl has the same salty taste as NaCl and is characterized by relatively offensive side tastes of acridity, metallicity, and bitterness (Rasheed et al., 2020). Likewise, NaCl and KCl also significantly reduce the plants’ morphological attributes, although the reduction in plants’ height and number of branches was not correlated linearly with increasing concentrations. Previously, it was reported that treatment with 300 mM KCl in Chenopodium album reduced growth and significantly reduced carotenoid levels (Yao et al., 2010). With rising concentrations of 50, 100, and 150 mM of KCl salt, the root and shoot growth of Carthamus tinctorius L. was also reduced (Leblebİcİ et al., 2021). The growth of Triticum aestivum L. was reduced by more than 60 ppm of KCl (Rasheed et al., 2020). When KCl is available in the soil, the plant experiences an overload of K+ accumulation in the cytoplasm, which destroys the K+/Na+ homeostasis and causes ion toxicity. Further, high KCl also causes the physiological drought condition in plants, causing osmotic stress, which leads to decreases in chlorophyll content and RWC and increases in EL, proline content, and DPPH activity in M. longifolia. According to previous research, the chlorophyll content decreases with KCl treatment in Malus hupehensis and is recovered by the application of exogenous strigolactones (Ma et al., 2022), whereas the proline content increases with 50 mM and 75 mM KCl treatment in pomegranate varieties (Dichala et al., 2022).
The present study suggests that M. longifolia can withstand high MgSO4 concentrations (100 mM), and the negative impact of excess salt is as prominent as in the case of other salts such as NaCl, KCl, and CaCl2. Like Na+ and K+, the excessive concentration of Mg2+ in soil also alters the ion balance in the cytoplasm and affects several biosynthetic processes, resulting in a decrease in photosynthetic pigment and RWC in M. longifolia. Magnesium (Mg2+) is an important plant nutrient involved in a variety of physiological processes, and its deficiency can harm crop quality and yield (Jezek et al., 2015). Mg2+ has an impact on several metabolic processes and reactions, such as photophosphorylation (which results in ATP synthesis in chloroplasts), photosynthesis-based fixing of carbon dioxide (CO2), protein formation, chlorophyll development, phloem loading, photoassimilate partitioning and consumption, the production of reactive oxygen species, and photooxidation in leaf tissues (Tang et al., 2012). But excessive amounts of Mg2+ in soil result in Mg2+ toxicity in plants. Serpentine soil is a rich source of magnesium because of weathering ultramafic rocks, which contain at least 70% ferromagnesian composition. High levels of soil Mg2+ inhibit the uptake of Ca2+ by the plant (Brady et al., 2005). The growth of Echinochloa species was also reduced by excess MgCl2 or MgSO4 in the culture solution (30 mM), leading to symptoms like calcium deficiency. However, rice cultivars grew only 54%–67% slower than the control, and excess Mg2+ in the culture solution did not mimic the symptoms of Ca2+ deficiency (Kobayashi et al., 2005). Additionally, magnesium overdose caused coppery coloration and defoliation during the final stages of toxicity (Selvaraj and Sankar, 2010).
The Mg2+ concentration of 1.5 mM is considered optimal for Arabidopsis growth, and its lower or higher concentrations can interfere with numerous reaction processes, including ion uptake, starch production, and degradation, and it might be involved in reorganizing plant morphology (Guo et al., 2014). In leaves, Mg2+ toxicity caused overly rapid starch and sugar breakdown. Starch biosynthesis enzymes like SS1, SS2, GBSS1, and APL1 were significantly suppressed by Mg2+ toxicity, but AtAMY1 and BAM1 were significantly increased. Several genes that code for the phytohormone biosynthetic enzymes are significantly increased by magnesium toxicity, such as ethylene (1-aminocyclopropane-1-carboxylate synthase), jasmonic acid (lipoxygenase), and ABA (9-cis-epoxycarotenoid dioxygenase) (Guo et al., 2015).
Approximately 12.5 mM CaCl2 has a beneficial effect on plant height in M. longifolia. Although its increasing concentrations of 25, 50, and 100 mM hampered the growth and development of Mentha. The symplastic pathway has been shown to increase chlorine transport at high salinities (Geilfus, 2018). According to previous documentation, CaCl2-treated Callistemon citrinus reduces height, dry weight, and number of leaves (25.4%, 33.2%, and 60.7%, respectively) in comparison to non-salinized control plants. Moreover, in Viburnum lucidum, the nutrient solution with 53.33 mM CaCl2 is also responsible for the reduction in plant height, the number of leaves per plant, shoot dry biomass, and the relative growth compared to the control plant (Cirillo et al., 2019). CaCl2 significantly reduces canopy volume, total leaf area per plant, leaf dry weight, and plant height in C. citrinus (De Micco et al., 2021). The extra Ca2+, which is unlikely to create toxicity, can restrict the intake or accessibility of other minerals such as K+ in V. lucidum or PO4 3− in C. citrinus, contributing to a restrained relative growth rate (RGR) (White and Broadley, 2003). Based on our data, like NaCl and KCl, moderate to high CaCl2 levels in the soil create an adverse impact on photosynthetic pigment content and RWC but also increase the El, proline content, and DPPH scavenging activity.
Volatile compounds are synthesized in response to various environmental factors, such as soil minerals, light intensity, climatic conditions, and soil salinity. In aromatic plants, these factors affect oil yields and composition differently (Çoban and Baydar, 2016). The EO production in M. longifolia was greatly reduced with 100 mM NaCl, KCl, and CaCl2, respectively. This may be because of the reduction in photosynthetic pigment, which leads to lesser photosynthate assimilation, resulting in decreased biosynthesis of EO. A similar study documented that irrigation with 100 mM NaCl reduced EO yield in Salvia (Taarit et al., 2009); 150 mM NaCl treatment reduced EO in Mentha piperita L. (Çoban and Baydar, 2016); and in Lallementia iberica (Paravar et al., 2022).
However, the low concentrations (12.5 mM) of NaCl, KCl, MgSO4, and CaCl2 led to increased essential oil yields in M. longifolia. This may be because the low concentrations of these salts’ ions support the mycorrhizal association and humic substances, which benefit root ramification and improve water and phosphorous uptake (Hazzoumi et al., 2015). Moreover, it is possible to think of oil yield augmentation at moderate salt concentrations as a salinity adaptation feature. Free volatiles are glycosylated and kept in cell vacuoles. These contribute to cellular expansion, which lessens the impact of the osmotic stress brought on by salt (Biswas et al., 2011). According to an essential oil GC–MS analysis of M. longifolia, it was found that carvone and limonene are the most dominant compounds. The percentage of both compounds is highly variable with different salt treatments. A carvone is produced biochemically in three steps: geranyl pyrophosphate is converted into (−)- limonene by limonene synthase, which is then hydroxylated into (−)-trans carveol by limonene-6-hydroxylase, which is then dehydrated by isopiperitenol dehydrogenase into (−)-carvone. (Bouwmeester et al., 1998). The biosynthesis of carvone and limonene is interrelated as limonene is the precursor of carvone (Delfine et al., 2022). KCl, NaCl, and MgSO4 at high concentrations inhibit limonene’s conversion to carvone, while NaCl at 50 mM supports limonene’s conversion to carvone at its best.
Including all morphological and physicochemical findings, it appears that salinity may adversely affect water uptake, membrane integrity, and biochemical pathways, resulting in a decrease in growth and biomass. Additionally, salinity results in nutritional imbalance, excessive ROS formation, and inhibition of enzymatic activities, all of which have a negative impact on biological membranes and cellular components and lower biomass output (Alzahrani et al., 2019; Kumar et al., 2021).
5 Conclusion
Salinity stress decreased FW, DW, RWC, and pigment content but increased accumulation of essential oil, especially its main components (carvone and D-limonene), EL and DPPH activity of M. longifolia plants. Salt concentrations of 12.5 mM and 25 mM stimulated production of essential oils, especially carvone and D-limonene. It may be concluded that M. longifolia is tolerant of mild soil salinity; thus, we may recommend its cultivation in saline soils. Future studies may be taken to further understand the molecular basis for increased essential oil accumulation in saline environments, including deciphering the regulatory networks.
Data availability statement
The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.
Author contributions
RS carried out most of the experimental work and analysis as well as wrote the manuscript and prepared the figures. SA helped RS in carrying out molecular analysis of this research and manuscript writing. SL and GR helped RS in carrying out experimental works and preparation of manuscript. AG carried out GC–MS/MS analysis. SG and RB designed the study, supervised RB, SA, SL, and GR also proofread the manuscript and figures. All authors contributed to the article and approved the submitted version.
Funding
The study was funded by Project HCP007 (Aroma Mission Phase 2) of the Council for Scientific and Industrial Research. The manuscript was reviewed and approved by Institutional Publication Committee with the reference number CSIR-IIIM/IPR/00552 Dated:03/27/2023.
Acknowledgments
The authors would like to thank Ranjeet and Bittu Ram for aiding in growing the planting material. RS thanks UGC-CSIR for Senior Research Fellowship. SA and SL thank CSIR India for Senior Research Fellowship. SG and RB are thankful to CSIR-IIIM and CSIR for funding.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
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Keywords: salt stress, growth, essential oil, physicochemical, biochemical, metabolites
Citation: Singh R, Ahmed S, Luxmi S, Rai G, Gupta AP, Bhanwaria R and Gandhi SG (2023) An assessment of the physicochemical characteristics and essential oil composition of Mentha longifolia (L.) Huds. exposed to different salt stress conditions. Front. Plant Sci. 14:1165687. doi: 10.3389/fpls.2023.1165687
Received: 14 February 2023; Accepted: 27 March 2023;
Published: 18 April 2023.
Edited by:
Sonal Mishra, Central University of Jammu, IndiaReviewed by:
Praveensingh Hajeri, University of Minnesota Twin Cities, United StatesDilfuza Jabborova, Academy of Sciences Republic of Uzbekistan (UzAS), Uzbekistan
Copyright © 2023 Singh, Ahmed, Luxmi, Rai, Gupta, Bhanwaria and Gandhi. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Sumit G. Gandhi, c3VtaXRAaWlpbS5hYy5pbg==; c3VtaXRnYW5kaGlAZ21haWwuY29t; Rajendra Bhanwaria, cmJoYW53YXJpYUBpaWltLnJlcy5pbg==
†These authors have contributed equally to this work