Abstract
Salinity is extremely hazardous to agriculture worldwide and its expanding constantly. Soil of almost 100 countries facing salinity problem including Pakistan. Cyperus laevigatus also act as salinity indicator species is a naturally adapted halophyte dispersed in subtropical regions of world. Six populations of C. laevigatus were collected from different saline habitats to evaluate adaptations regarding anatomical and physiological characteristics. C. laevigatus is perfectly adapted to harsh environmental conditions like dry barren soils, saline lakes, hyper-saline wetlands and salt marshes. Ecological success of this species is due to plasticity in physiological and anatomical characteristics to adapt variable environmental conditions. C. laevigatus is a halophyte, exhibited increased biomass production in moderately saline habitat. Higher uptake of K+ occurs to compensate the uptake of Na+ ion contents, a striking feature of salt-tolerant and halophytic species. Accumulation of osmoprotectants like proline, free amino acids, soluble sugar and protein contribute significantly to osmotic adjustment. Stem thickness enhanced as salinity level of habitat increased to store water in parenchymatous tissues under physiological drought. Intensive sclerification in root cortex provide mechanical strength to plant as well as prevent the radial leakage of water. Well-developed aerenchyma, increased vascular bundle area, broader vessels, small and dense stomata are critical to cope with environmental hazards. Population of Jahlar lake showing maximum biomass production indicate that this species grows better in moderate salinities. Therefore, this species will prove very useful for revegetation of salt affected rangeland and prairies by direct growth of such halophytic ecotypes.
Keywords: Aerenchyma, Plasticity, Sclerification, Osmoprotectants, Salt marshes
1. Introduction
Salinity is one of the major challenges for agricultural crops due to its effect on yield and sustainability particularly in arid and semi-arid regions of world (Iqbal et al., 2015, Ahmad et al., 2019, Adhikari et al., 2020). During 19th century, salinity emerged as leading problem in Pakistan due to limited crop production and loss in economy (Safdar et al., 2019). Salt-affected habitats like saline drylands and salt wetlands in Pakistan recognized by the presence of salinity indicator species such as Cyperus lavigatus (Khan and Qaiser, 2006). In other regions of the world common salt indicator species are Sporobolus virginicus, Juncus acutus, Salsola vermiculata, Salicornia europaea and Suaeda australis (Aslamsup et al., 2011). Saline soil imparts several harmful effects on plants growth and development because of reduced water uptake and excessive ions absorbance, which ultimately leads to side effects on cellular level (Alam et al., 2020). Salinity can cause disturbance in nutritional requirement of plants (Saleem et al., 2019, Ahanger et al., 2020, Ali et al., 2020a, Kaya et al., 2020). NaCl stress is one of the most abundant because saline soils are dominated with high contents of Na+ and Cl- those are found in excessive amount than plants requirement (Alam et al., 2019, Safdar et al., 2019). The higher quantity of salt in rhizosphere leads to the disturbance in aqueous and ionic balance like toxicity, ionic disparity and hyper-osmotic stress (Parihar et al., 2015). Due to these disturbances, enzyme activities and plant chemical reactions affect adversely (Liu et al., 2020, Rehman et al., 2020a, Saleem et al., 2020b, Saleem et al., 2020d, Saleem et al., 2020e).
Halophytes can endure higher concentrations of salt and have ability to flourish in stressed environment by accumulation of some important ions and osmolytes (Usman et al., 2018). Membrane integrity, K+/Na+ selectivity and osmoregulation maintained by higher contents of Ca2+ in plants growing under salt stress (Safdar et al., 2019, Yaseen et al., 2020). Soluble proteins, sugars and other solutes are crucial in osmoregulation such as enhanced water uptake and retention, protection of macromolecules structures which can be damaged under salt stress (Jabeen and Ahmad, 2017, Saleem et al., 2020c). Salt stress can cause adverse effects on plant morphological and anatomical features such as stunted root and shoot growth, reduced fruit and vegetable yield, shrinkage in stem diameter, smaller root cortex and inhibition of vascular growth (Iqbal et al., 2015, Zafar et al., 2015). Halophytes tolerate salinity stress by the development of specific anatomical structures like succulence in shoot and midrib, development of aerenchyma, larger vascular bundles, increased phloem and metaxylem area and intensive sclerification (Parida and Das, 2005, Imran et al., 2019, Mohamed et al., 2020a). Stomatal area, density and orientation contribute a lot in process of salinity tolerance (Mohamed et al., 2020b).
Cyperus laevigatus L. also known as smooth flat sedge is a perennial sedge dispersed in subtropical regions of world with hot climate. It flourishes mostly in aquatic habitats such as waterlogged soil, brackish water, coastal areas, flood plains and mud flats (Badr et al., 2020). This species used for the treatment of wetland ecosystems where NH4+ concentrations are high (Gamal et al., 2015). The objective of the present study was to evaluate adaptive components of salinity tolerance in differently adapted populations of Cyperus laevigatus.
2. Materials and methods
2.1. Collection of samples
Six populations of Cyperus laevigatus were collected from different ecological regions of the province Punjab, viz., Haroonabad, Khushab, Jahlar Lake, Pakka anna, Kalar Kahar Lake and Sahianwala. These regions were selected on the basis of widespresd distribution of this species. The physico-chemical properties from rhizosphere of Cyperaceae species collection sites in the Punjab are presented in Table 1 & Fig. 1.
Table 1.
Habitat | Har | Khu | Jha | PA | KK | Sah |
---|---|---|---|---|---|---|
pH | 9.2 | 7.3 | 7.4 | 8.5 | 7.8 | 8.3 |
ECe (dS m−1) | 3.4 | 14.2 | 16.8 | 32.7 | 37.3 | 46.3 |
SP | 33.7 | 38.4 | 35.2 | 32.3 | 36.8 | 32.3 |
Na+ (mg g−1 d.wt.) | 177.4 | 3210.5 | 2844.6 | 3733.7 | 4023.7 | 5759.1 |
K+ (mg g−1 d.wt.) | 58.7 | 255.8 | 249.3 | 345.2 | 173.6 | 371.6 |
Ca2+ (mg g−1 d.wt.) | 108.7 | 155.3 | 277.6 | 68.9 | 133.7 | 366.9 |
Cl- (mg g−1 d.wt.) | 433.2 | 1390.1 | 1611.8 | 1922.4 | 2029.8 | 2528.1 |
Annual rainfall (mm) | 191 | 395 | 450 | 310 | 485 | 375 |
Elevation (m a.s.l.) | 178 | 174 | 950 | 172.6 | 734.2 | 190.4 |
Coordinates | 29° 60′ 81″ N 73° 14′ 68″ E | 32° 17′ 55″ N 72° 21′ 3″ E |
33° 38′ 17″ N 72° 20′ 38″ E | 31° 15′ 63″ N 71° 50′ 19″ E |
32° 46′14″ N 72° 42′ 32″ E |
31° 39′ 47″ N 73° 13′ 31″ E |
Habitat description | Situated on edge of Cholistan desert, sandy soil with drought tolerant vegetation, hot climate | Dry barren hills with sandy soil, very sparse vegetation mostly salt-tolerant | Salt-water lake situated in mountains, dominated by sedges and salt-tolerant grasses, cooler climate | Hyper-saline wetland, reclaimed by Leptochloa fusca. | Hyper-saline lake surrounded by hills, dominated by halophytes, cooler climate | Situated near Faisalabad, highly saline waterlogged area dominated with salt-tolerant and halophytic species |
2.2. Shoot water relations
Scholar-type pressure chamber was utilized for the determination of shoot water potential of each replicate of six habitats. For the determination of osmotic potential same shoot was frozen at −20 °C for one week. Then frozen shoot was thawed, and cell sap extracted to determine osmotic potential by using vapor pressure osmometer (Wescor 5500). Value of turgor potential obtained by subtracting osmotic potential from the water potential.
2.3. Plant ionic content
0.1 g of shoot and root material from each sample was dried and ground, then it was subjected to digestion with conc. H2SO4 following Wolf (Wolf, 1982) to record the ionic contents values. Na+, K+ and Ca2+ were determined by flame photometer (Jenway, PFP-7).
2.4. Organic osmolytes
Total amino acid was determined according to the method used by Moor and Stein (Moore and Stein, 1948). 1.0 g fresh leaves chopped into 10 mL citrate buffer, incubated at room temperature for one hour and then centrifuged at 15000 rpm for 10 min at 15 °C. The supernatant then separated and used for the determination of free amino acids. 1.0 mL extract and ninhydrin solutions were added in vessel, covered with aluminum foil, and heated for 20 min in boiling water bath. The vessel was then cooled, 5 mL diluent added and subjected to incubation for 15 min at room temperature. OD was recorded at 570 nm on a UV–visible spectrophotometer (Hitachi 220, Japan).
To determine the total soluble proteins method of Lowry et al. (Lowry et al., 1951) was used. 0.2 g fresh leaves chopped in 5 mL 0.2 M phosphate buffer (7.0 pH). Chopped leaf material was then centrifuged at 5000 rpm for 5 min. 1.0 mL of supernatant from each sample and copper reagents added in a vessel, mixed thoroughly, and kept still for 10 min at room temperature. After that 0.5 mL of Folin-phenol reagent taken, mixed and then subjected to incubation for 30 min at room temperature. OD was recorded at 620 nm on a spectrophotometer (Hitachi 220, Japan).
Yemm and willis (Yemm and Willis, 1954) method was used for the determination of total soluble sugars. 0.1 g of fresh plant undergone extraction with 80% ethanol. The extracted material was kept in incubator at 60 °C for 6 h. This material was used to estimate the quantity of soluble sugars. The extract was mixed with anthrone reagent (6 mL) and then warmed for 10 min in boiling water. This was subjected to cooling with ice cubes for 10 min and then kept in incubator for 20 min at 25 °C. Optical density was observed at the wavelength of 625 nm on a spectrophotometer (Hitatchi, 220, Japan).
The estimation of proline contents was analyzed according to method performed by Bates et al. (Bates et al., 1973). 0.5-gram leaves mixed and homogenized with 3% sulfo-salicylic acid (10 mL). The resulting mixture filtered by Whatman no. 2 filter paper. 2 mL of acid ninhydrin solution (1.25 g ninhydrin in 30 mL glacial acetic acid), 2 mL of glacial acetic acid and 20 mL of 6 M orthophosphoric acid reacted with 2 mL filtrate at 100 °C for one hour. Ice bath used to complete this reaction. Product of this reaction was mixed with toluene (4 mL), and then fiercely mixed while air is passing through it for 1–2 min. After that toluene was extracted from this reaction, heated at 25 °C and absorbance was observed at 520 nm.
2.5. Anatomical parameters
For anatomical investigation root, stem, bract and leaves were washed and preserved in (FAA) formalin acetic alcohol. Free hand sectioning technique was used to prepare permanent slides. Dehydration of transverse and epidermal sections was processed through series of ethanol grades. Standard double-staining procedure was adopted for staining the sections using safranin and fast green stains to differentiate between lignified and other tissues. Photographs of these slides was taken by camera-equipped compound microscope (Nikon 104, Japan). Anatomical data were recorded by ocular micrometer (Fig. 2).
2.6. Statistical analysis
Samples for anatomical studies were collected from three different sites of each habitat and then data were subjected to analysis of variance (one-way ANOVA) using Microsoft Exceland RDA (Redundancy analysis) using XLSTAT. The heat-map analysis between various variables are constructed using RStudio.
3. Results
3.1. Morphological characteristics
Shoot fresh weight showed a notable variation in populations of C. laevigatus collected from different habitats of Punjab. The highest shoot biomass was observed in those populations which were growing in Jhalar Lake. The lowest biomass was recorded in population of Pakka Anna. There was a significantly varied response of root fresh weight among habitats as the maximum weight was reported in Jhalar Lake, while population of salt marsh like Pakka Anna showed the minimum growth (Table 2).
Table 2.
Har | Khu | Jha | PA | KK | Sah | F-ratio | |
---|---|---|---|---|---|---|---|
Morphological characteristics | |||||||
Shoot fresh weight (g plant−1) | 10.8b | 9.2c | 14.9a | 8.7d | 10.7bc | 10.4bc | 366.2*** |
Root fresh weight (g plant−1) | 0.96d | 1.2bc | 4.1a | 1.3b | 1.1c | 0.91de | 1223.7*** |
Water Potential | |||||||
Shoot water potential (-Mpa) | 1.4c | 1.5b | 1.6a | 1.6a | 1.4c | 1.5b | 169.1*** |
Shoot osmotic potential (-Mpa) | 1.2a | 1.2a | 1.1b | 1.2a | 0.8c | 0.6d | 21.7*** |
Shoot turgor potential (Mpa) | 0.24d | 0.29 cd | 0.48bc | 0.38c | 0.56b | 0.92a | 18.7*** |
Ionic Contents | |||||||
Shoot Na+ (mg g−1 d.wt.) | 21.2f | 25.5d | 24e | 32.5a | 30.2b | 27.7c | 11.4*** |
Root Na+ (mg g−1 d.wt.) | 16.5b | 14c | 14.5c | 15.2bc | 18.5a | 18.2a | 3.8* |
Shoot Ca2+ (mg g−1 d.wt.) | 20.5b | 21.5ab | 15.3d | 19 cd | 18.3c | 22.5a | 3.3* |
Root Ca2+ (mg g−1 d.wt.) | 4.2b | 4.1b | 2.9d | 3.7c | 4.5a | 4.3a | 2.2NS |
Shoot K+ (mg g−1 d.wt.) | 8d | 10b | 9.8c | 8.5 cd | 15a | 10.5ab | 13.4*** |
Root K+ (mg g−1 d.wt.) | 22d | 27.5c | 30.5b | 27.5c | 34.2a | 29.5bc | 10.1*** |
Organic Osmolytes | 645.7d | 1283.3c | 1900ab | 1895.8ab | 1950a | 1726.7b | 35.5*** |
Total free amino acids (µg g-1f. wt.) | |||||||
Proline (µmol g-1f. wt.) | 102de | 113.9d | 190.4b | 187b | 255a | 136c | 9.3** |
Total soluble proteins (µg g-1f. wt.) | 948bc | 600d | 732 cd | 1020a | 960b | 792c | 1.4NS |
Total soluble sugars (mg g−1 d. wt.) | 27.7b | 26.3bc | 25.3c | 30.1a | 27b | 27.4b | 0.97NS |
Means sharing similar letters in each row are statistically not significant.
* = Significant at p < 0.05, ** = significant at p < 0.01, *** = significant at p < 0.001, NS = not significant.
3.2. Water relation traits
Jhalar Lake and Pakka Anna exhibited highest values of shoot water potential, which have no significant variation from other collection sites of C. laevigatus (Table 2). The maximum shoot osmotic potential was reported in Haroonabad, Khushab and Pakka Anna populations, with minimum values observed in Sahianwala population. Sahianwala surpassed all the other populations regarding shoot turgor potential. All other habitats varied significantly, with least potential observed in Haroonabad.
3.3. Ionic content
Pakka Anna population was reported with highest Na+ contents in shoots. It showed variation from 21.2 to 32.5 mg g−1 d.wt., with least values noted in Haroonabad (Table 2). Root Na+ ranges in quantity from 18.5 to 14 mg g−1 d.wt. in Kalar Kahar Lake and Khushab respectively. This character is not much diverse among different habitats of C. laevigatus. Shoot and root Ca2+ was found the maximum in population of Sahianwala, with the minimum values observed in Jhalar Lake. There was no significant difference among habitats regarding root Ca2+. Kalar Kahar Lake exhibited the highest shoot K+ and root K+ with slight variation among other populations of C. laevigatus. Population of Haroonabad was recorded with the least values of shoot K+ and root K+.
3.4. Organic osmolytes
Total free amino acids and proline accumulate maximally in population collected from Kalar Kahar Lake (Table 2). Free amino acids differ notably among other habitats, with least values noted in Haroonabad. The saline habitat, Pakka Anna surpassed all the other habitats of C. laevigatus regarding soluble proteins and sugars but showed no significant variation among selected sites.
3.5. Root anatomical characteristics
Root anatomical features varies significantly among selected habitats of C. laevigatus (Table 3 & Fig. 3). Root and cortical thickness was observed the maximum in Kalar Kahar Lake population, while least thickness recorded in Haroonabad. Population collected from Haroonabad depicted thickest epidermis of root along with thinnest vascular region and the least aerenchyma area. The maximum endodermal thickness, metaxylem area, vascular region thickness and aerenchymatous area reported in populations of Kalar Kahar Lake. Khushab population depicted the minimum cortical cell size, endodermal thickness and vessels size. Population collected from Pakka Anna surpassed all other collection sites regarding cortical cell area. The Jhalar Lake was observed with minimum values of Epidermal thickness.
Table 3.
Har | Khu | Jha | PA | KK | Sah | F-ratio | |
---|---|---|---|---|---|---|---|
Root Anatomy | |||||||
Root thickness (µm) | 261.4 cd | 310.5c | 449.3bc | 473.9b | 620.9a | 433.0bc | 81.2*** |
Epidermal thickness (µm) | 16.3a | 15.5ab | 6.5 cd | 8.9c | 15.5ab | 12.2b | 72.8*** |
Cortical thickness (µm) | 98.0 cd | 106.2c | 196.1ab | 204.2ab | 1253.3a | 179.7b | 162.5*** |
Cortical cell area (µm2) | 288.8e | 209.6f | 504.9c | 629.7a | 440.9d | 587.7b | 85.9*** |
Endodermal thickness (µm) | 7.3d | 4.1f | 8.9b | 6.5e | 9.8a | 8.2c | 18.5*** |
Metaxylem area (µm2) | 94.7d | 47.5de | 210.1c | 334.9b | 551.0a | 199.6c | 196.3*** |
Vascular region thickness (µm) | 15.5d | 23.7c | 17.9 cd | 34.3b | 44.9a | 31.9bc | 554.0*** |
Aerenchymatous area (µm2) | 2311.1c | 2646.7bc | 3150.2b | 0 | 4618.7a | 0 | 140.6*** |
Stem Anatomy | |||||||
Stem thickness (µm) | 547.4 cd | 637.3bc | 580.1c | 612.7bc | 645.4b | 743.5a | 22.7*** |
Epidermal thickness (µm) | 12.2b | 10.6bc | 8.2 cd | 17.1a | 15.5ab | 8.9c | 58.1*** |
Cortical cell area (µm2) | 2014.3b | 1410.1de | 1783.5c | 1636.6 cd | 2360.4a | 1516.5d | 96.3*** |
Vascular bundle area (µm2) | 1038.8d | 752.9e | 734.6ef | 2403.4b | 1737.3c | 2634.2a | 630.3*** |
Metaxylem area (µm2) | 58.0b | 59.1b | 75.9a | 44.4c | 68.5ab | 52.3bc | 2.9NS |
Sclerenchyma thickness (µm) | 8.9f | 20.4b | 23.7a | 17.9c | 15.5d | 11.4e | 136.80*** |
Chlorenchyma thickness (µm) | 25.3bc | 23.7c | 20.4 cd | 38.4ab | 42.5a | 32.7b | 346.40*** |
Stomatal area (µm2) | 419.9e | 629.7c | 797.5b | 588.8d | 918.1a | 920.8a | 75.85*** |
Stomatal density | 14.7c | 11.7 cd | 19.7b | 16.7bc | 18bc | 27a | 34.35*** |
Bract Anatomy | 650.9a | 160.7d | 294.1bc | 291.4bc | 253.3c | 422.1b |
187.7*** |
Bract thickness (µm) | |||||||
Epidermal thickness (µm) | 11.2c | 8.4d | 16.6ab | 17.9a | 16.3ab | 15.2b | 23.9*** |
Cortical cell area (µm2) | 1007.3b | 639.1 cd | 818.5c | 734.6bc | 755.6bc | 2242.4a | 473.1*** |
Vascular bundle area (µm) | 671.6e | 1442.6ab | 1463.6a | 760.8d | 1091.2c | 1321.9b | 147.2*** |
Metaxylem area (µm2) | 26.0 cd | 50.7ab | 52.3a | 29.7c | 10.8d | 42.3b | 10.4*** |
Chlorenchyma thickness (µm) | 21.3c | 22.7c | 18.4d | 38.5a | 28.4b | 29.7b | 11.4*** |
Aerenchyma area (µm2) | 3410.4ab | 3092.5b | 4041.8a | 2835.6c | 1765.7d | 0 | 57.7*** |
Leaf Sheath Anatomy | 85.8 cd | 73.5d | 163.4a | 89.9c | 130.7b | 81.7 cd | 55.72*** |
Leaf sheath thickness (µm) | |||||||
Upper epidermal thickness (µm) | 8.9e | 15.5b | 12.2d | 14.7c | 16.3a | 8.2ef | 53.70*** |
Lower epidermal thickness (µm) | 12.2c | 14.7b | 8.9de | 9.8d | 16.3a | 7.3e | 54.50*** |
Cortical Cell Area (µm2) | 503.8a | 231.1 cd | 219.6d | 262.6c | 283.5bc | 385.8b | 53.71*** |
Aerenchyma Area (µm2) | 3543.6 cd | 3674.7c | 10073.0a | 4199.1bc | 5772.5b | 2206.2d | 112.78*** |
Vascular bundle area (µm2) | 472.4d | 903.5c | 1564.3a | 1070.2bc | 866.7 cd | 1101.7b | 173.77*** |
Metaxylem area (µm2) | 10.8f | 16.1e | 42.3b | 52.8a | 26.0d | 33.4c | 11.94*** |
Means sharing similar letters in each row are statistically not significant.
* = Significant at p < 0.05, ** = significant at p < 0.01, *** = significant at p < 0.001, NS = not significant.
3.6. Stem anatomical characteristics
The thickest stem was reported in population of Sahianwala and epidermis in population of Pakka Anna (Table 3 & Fig. 3). Population of Haroonabad showed the minimum stem thickness and stomatal area. Cortical cell area, chlorenchyma thickness and stomatal area was reported the maximum in Kalar Kahar Lake population (Table 3 & Fig. 5). Khushab population depicted lowest cortical cell area and least number of stomata. Vascular bundle area, stomatal area and stomatal density values were recorded the maximum in Sahianwala population, with least thickness of sclerenchymatous tissues. The narrowest vessel was observed in population of Pakka Anna among all the selected habitats. The minimum values for epidermal thickness, vascular bundle area and chlorenchyma thickness was observed in Jahla Lake population. Broader vessels and thicker sclerenchyma tissues were also noted in population of this habitat.
3.7. Bract anatomical characteristics
Haroonabad population possessed the highest values for bract thickness and lowest values for vascular bundle size and chlorenchyma thickness (Table 3 & Fig. 4). Population collected from Sahianwala surpassed all other habitats regarding cortical cell area. Narrow vessels and smaller aerenchyma observed in Kalar Kahar Lake population. Epidernal and chlorenchyma thickness was reported the maximum in Pakka Anna population. Population of Jhalar Lake depicted larger vascular bundles, broader vessels and the maximum sized aerenchyma. Bract thickness, epidermal thickness and cortical cell area recorded with the minimum values in population of Khushab.
3.8. Leaf sheath anatomical characteristics
Population of Jhalar lake had leaf sheath with the maximum thickness as compared to other collection sites (Table 3 & Fig. 4). The maximum values for aerenchyma area and vascular bundle area were also noted in this site, along with smallest cortical cells. Broader and narrower vessels reported in populations of Pakka Anna and Haroonabad respectively. Upper and lower epidermal thickness was recorded with higher values in population of Kalar Kahar Lake. Sahianwala population possessed the minimum aerenchyma area, upper and lower leaf sheath thickness. The thinnest leaf sheath was observed in population collected from riverbank of Khushab. Haroonabad population showed maximum cortical cell area and minimum vascular bundle area.
3.9. Relationship among habitats and plant structural & functional attributes
A heat-map analysis was constructed to quantify the relationship between different morpho-physiological and anatomical traits of C. laevigatus collected from different regions of Punjab district are presented in Fig. 6. Almost most of parameters are showing no relationship or negative relationship with their habitat. However, some growth parameters, ions, osmolytes and anatomical traits showed a significant positive relationship which were collected from Jahlar lake. In this heat-map analysis blue colour is indicating no significant difference while turquoise is showing a significant postive relationship with selected habitats. This relationship is showing a close connection between different parameters of Cyperus laevigatus to selected habitats of Punjab.
3.10. Association between soil and plant morpho-physiological & anatomical parameters
Redundancy analysis (RDA) ordination biplot illustrated the impact of soil characteristics of diverse habitats on physiological and morpho-anatomical attributes of Cyperus laevigatus (Fig. 7 & Fig. 8). Root fresh weight and sheet fresh weight strongly associated with annual rainfall at Jahlar and Kalar Kahar lake. Water and turgor potential possessed association with soil EC, Na+, Ca2+, K+ and Cl- contents. Shoot and root K+ associated strongly with annual rainfall. Root Ca2+ depicted relationship with soil pH. Root thickness, cortical thickness and metaxylem area possessed strong association with annual rainfall at Kalar Kahar and Jahlar lake. Root aerenchyma area had association with Khushab. Stem thickness, vascular bundle area, chlorenchyma thickness and stomatal density exhibited strong relationship with soil EC, Na+, Ca2+, K+ and Cl- contents at Sahianwala. Bract thickness associated with soil pH at Haroonabad. Epidermal thickness, cortical cell area and chlorenchyma thickness associated strongly with soil EC, Na+, Ca2+, K+ and Cl- contents at Pakka Anna. Leaf sheath thickness, aerenchyma area and vascular bundle area had strong relationship with rainfall at Jahlar and Kalar Kahar lake. Lower epidermal thickness showed association with saturation percentage at Khushab.
4. Discussion
Ecotypic variation can be determined by investigating structural and functional modifications of different populations of a species (Rana et al., 2020a). Structural features are most vulnerable to surrounding climatic factors and strongly respond to abiotic stresses (Ali et al., 2020b, Rehman et al., 2020, Saleem et al., 2020a). Each population of Cyperus laevigatus showed different structural and functional response, it can be determined that adaptive characteristics have been fixed during evolutionary process and this can be a reason behind variable developmental behavior (Badr et al., 2020).
Haroonabad is a non-saline habitat, located at edge of Cholistan desert with smaller annual rainfall and soil with good saturation percentage. Higher osmotic potential in this population leads to better growth and biomass production (Hussain et al., 2016). K+ ions and osmolytes found in very low quantity because these plants are not facing any environmental stress. Water conservation is not the main strategy of Haroonabad population because its not facing the physiological drought caused by salinity (Corrêa et al., 2017). This population exhibited less development of vascular tissues, aerenchyma and root cortex which indicates non-stressful environment of this habitat (Mohamed et al., 2020a). Stomatal area of this population is much decreased which may be beneficial during less availability of water (Khan et al., 2019). Larger cortical cells of leaf sheath maintain turgor of plants when they face water scarcity (Liang et al., 2018, Nazar et al., 2020).
Saline soil of Khushab reduced biomass production of C. laevigatus. It receives good annual rainfall but due to dry barren hills and salinity enough water is not available to plants. A moderate accumulation of K+ ions in this population may be for K+/Na+ selectivity for preventing excessive Na+ ion uptake (Alam et al., 2020). No noticeable alteration observed in anatomical features of this population but narrow xylem vessels are highly advantageous because wide vessels can be susceptible to collapse under physiological drought (Goharrizi et al., 2020, Rana et al., 2020b). Low stomatal density exhibited adaptation of this population to dry barren land, which is very effective for water conservation (Khan et al., 2019, Afzal et al., 2020).
Jahlar lake is a salt-water lake situated in mountains, dominated with sedges and salt-tolerant grasses. It receives moderately high annual rainfall. Maximum shoot water potential of this population contributes to the highest shoot and root fresh weight (Hussain et al., 2018). The thinnest root epidermis observed because water conservation not required due to availability of plenty of water. Broader vessels in vascular bundles involved in effective water movement when availability of water is sufficient (Ahmad et al., 2017). Aerenchyma formation in bracts and leaf sheath provide benefits to this population for supply of oxygen under hypoxic conditions. Aerenchyma development has been recorded in populations growing under salt stress (Mohamed et al., 2020b). Periphery of stem is highly sclerified that has contribution to water conservation as well as mechanical strength to plants (Gunes et al., 2006).
Pakka Anna is a hyper-saline wetland that is dominated by halophytes, receives sufficient annual rainfall. Plants were poorly developed with minimum shoot fresh weight most probably due to physiological stress caused by saline wetland and highest accumulation of Na+ ions in shoots (Parihar et al., 2015). Under salt stress, soluble proteins and sugars accumulated excessively to reduce the adverse effects of ROS (Ali et al., 2020a). Thick epidermal cells of stem minimize the water loss under shortage of water during physiological stress. Large cortical cells of root mostly possess larger vacuoles that may be advantageous for physiological drought under waterlogged soils (Ahmad et al., 2017). Enhanced chlorenchyma thickness observed in bract to fulfil the photosynthetic requirement because salt stress hinder the physiological mechanisms (Gunes et al., 2006).
Kalar Kahar is a hyper-saline lake, receives maximum annual rainfall as compared to other habitats. Population collected from the bank of lake exhibited ultimate tolerance to salt stress. There is excessive accumulation of Na+ contents in roots, toxicity of these ions nullified by the accumulation of Ca2+ and K+ ions (Zamin and Khattak, 2017). Higher accumulation of osmolytes like free amino acids and proline reported, that reveals high level tolerance to salt stress in population of Kalar Kahar (Szabados and Savouré, 2010). This population exhibited the maximum of mostly anatomical features like dermal thickness, mechanical tissues, vascular and storage tissues. All these anatomical features are essential for water conservation either by storage of water or by preventing water loss from plant body (Abid et al., 2018).
Sahianwala is located near Faisalabad, highly saline waterlogged salt marsh. It receives moderate annual rainfall, but saline soil restricted the biomass production of C. laevigatus. Higher accumulation of Ca2+ contents may take part in the neutralization of side effects caused by salt stress (Kamran et al., 2019). Stem growth observed maximum in this population to store the maximum amount of water in parenchymatous tissues for stressed environmental conditions (Hasanuzzaman et al., 2018). Larger vascular bundles with broader xylem vessels associated with enhanced water conductivity (Mohamed et al., 2020b). Increased stomatal size in this population may associated with efficient photosynthetic process (Kamran et al., 2019).
5. Conclusion
Cyperus laevigatus ecotypes exhibited higher level of plasticity in structural and functional features, which offer this species a great ability to flourish in variable stressed habitats. Populations of this species were collected from different saline habitats like dry barren soils, saline lakes, hyper-saline wetlands and salt marshes to evaluate anatomical modifications and ionic homeostasis. Each population revealed specific adaptations regarding anatomical and physiological characteristics, which exhibited its adaptability potential to harsh environmental conditions. Population of Jahlar lake showed maximum biomass production indicates that it grows better in moderate salinities. This species will prove very useful for revegetation of salt affected rangeland and prairies by direct growth of such halophytic ecotypes. Genes can be extracted from this species and incorporated to crops to enable them to grow in high salinities either by conventional breeding or advanced molecular biology approaches.
Ethics approval
Not Applicable
Consent to participate
All authors consent to participate in this manuscript.
Consent for publication
All authors consent to publish this manuscript in Saudi journal of Biological Science
Availability of data and material
Data will be available on request to the corresponding or first author
Code availability
Not Applicable
Authors' contributions
Sahar Mumtaz, Mansoor Hameed, Athar Mahmood conceived and designed the study and Fatima Batool, Syeda Fasiha Amjad and Abida Parveen critically revised the manuscript and approved the final version. Shakeel Ahmed, Abdulaziz Abdullah Alsahli, Mohammed Nasser Alyemeni and Humaira Yasmin executed the experiment and compiled data. Muhammad Hamzah Saleem supervised the experiment and Muhammad Arfan helped in sample collection and chemical analysis. All authors read and approve the same for publication.
Declaration of Competing Interest
The authors declared that there is no conflict of interest.
Acknowledgments
We gratefully acknowledge Higher Education Commission of Pakistan for providing financial assistance. The results reported in this paper are the part of Doctoral research work of Dr. Sahar Mumtaz. The authors also acknowledge Researchers Supporting Project number (RSP 2020/236), King Saud University, Riyadh, Saudi Arabia.
Footnotes
Peer review under responsibility of King Saud University.
Contributor Information
Sahar Mumtaz, Email: sahar_botany@yahoo.com.
Muhammad Hamzah Saleem, Email: saleemhamza312@webmail.hzau.edu.cn.
Fatima Batool, Email: fatima.batool@ue.edu.pk.
Athar Mahmood, Email: athar.mahmood@uaf.edu.pk.
Muhammad Arfan, Email: m.arfan@ue.edu.pk.
Shakeel Ahmed, Email: shakeel1177@uach.cl.
Humaira Yasmin, Email: humaira.yasmin@comsats.edu.pk.
Abdulaziz Abdullah Alsahli, Email: aalshenaifi@ksu.edu.sa.
Mohammed Nasser Alyemeni, Email: mnyemeni@ksu.edu.sa.
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