Next Article in Journal
Plant Growth-Promoting Rhizobacteria Improve Rice Response to Climate Change Conditions
Previous Article in Journal
The Growth Oscillator and Plant Stomata: An Open and Shut Case
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Comparative Evaluation of Antioxidant Status and Mineral Composition of Diploschistes ocellatus, Calvatia candida (rostk.) Hollós, Battarrea phalloides and Artemisia lerchiana in Conditions of High Soil Salinity

by
Nadezhda Golubkina
1,*,
Tatiana Tolpysheva
2,
Vladimir Lapchenko
3,
Helene Lapchenko
3,
Nikolay Pirogov
4,
Viacheslav Zaitsev
5,
Agnieszka Sękara
6,
Alessio Tallarita
7,
Vasile Stoleru
8,
Otilia Cristina Murariu
8 and
Gianluca Caruso
7
1
Federal Scientific Vegetable Center, Kubinka 143072, Russia
2
Department of Biology, Lomonosov Moscow State University, Leninskie Gory,1, Building 1, Moscow 119234, Russia
3
T.I. Vyazemsky Karadag Scientific Station, Nature Reserve RAS–Branch of A. O. Kovalevsky Institute of Biology of the Southern Seas of RAS, Feodosia 298188, Russia
4
Bogdinsko-Baskunchak Nature Reserve, Akhtubinsk 416532, Russia
5
Department of Hydrobiology and General Ecology, Astrakhan State Technical University, Tatisheva 16, Astrakhan 414025, Russia
6
Department of Horticulture, Faculty of Biotechnology and Horticulture, University of Agriculture, 31-120 Krakow, Poland
7
Department of Agricultural Sciences, University of Naples Federico II, 80055 Portici, Italy
8
“Ion Ionescu de la Brad” Iasi University of Life Sciences, 3 M. Sadoveanu Alley, 700440 Iasi, Romania
*
Author to whom correspondence should be addressed.
Plants 2023, 12(13), 2530; https://doi.org/10.3390/plants12132530
Submission received: 31 May 2023 / Revised: 26 June 2023 / Accepted: 28 June 2023 / Published: 3 July 2023
(This article belongs to the Section Plant Ecology)

Abstract

:
Natural reserves play a fundamental role in maintaining flora and fauna biodiversity, but the biochemical characteristics of such ecosystems have been studied in an extremely fragmentary way. For the first time, mineral composition and antioxidant status of three systematic groups of organisms, lichens (Diplischistes ocellatus), mushrooms (Calvatia candida and Battarrea phalloides) and wormwood (Artemisia lerchiana) have been described at the territory of Bogdinsko-Baskunchak Nature Reserve (Astrakhan region, Russia), characterized by high salinity and solar radiation, and water deficiency. Through ICP-MS, it was determined that scale lichen D. ocellatus accumulated up to 10–15% Ca, 0.5% Fe, 15 mg kg−1 d.w. iodine (I), 54.5 mg kg−1 Cr. Battarrea phalloides demonstrated anomalously high concentrations of B, Cu, Fe, Mn Se, Zn, Sr and low Na levels, contrary to Calvatia candida mushrooms accumulating up to 10,850 mg kg−1 Na and only 3 mg kg−1 Sr. The peculiarity of A. lerchiana plants was the high accumulation of B (22.23 mg kg−1 d.w.), Mn (57.48 mg kg−1 d.w.), and antioxidants (total antioxidant activity: 68.6 mg GAE g−1 d.w.; polyphenols: 21.0 mg GAE g−1 d.w.; and proline: 5.45 mg g−1 d.w.). Diploschistes ocellatus and Calvatia candida demonstrated the lowest antioxidant status: 3.6–3.8 mg GAE g−1 d.w. total antioxidant activity, 1.73–2.10 mg GAE g−1 d.w. polyphenols and 2.0–5.3 mg g−1 d.w. proline. Overall, according to the elemental analysis of lichen from Baskunchak Nature Reserve compared to the Southern Crimean seashore, the vicinity of Baskunchak Salty Lake elicited increased environmental levels of Cr, Si, Li, Fe, Co, Ni and Ca.

1. Introduction

The Bogdinsko-Baskunchak Nature Reserve, situated in the North-Eastern part of the Astrakhan region (Russia), occupies a territory of 18,478 ha and, since 2021, belongs to UNESCO World Heritage Sites. It is famous due to the Baskunchak Salt Lake which has a sodium chloride deposit that is 10–18 m thick and is characterized by a unique semi-desert climate, strong soil salinization, remarkable gypsum accumulation, dust winds, broad annual temperature range between −40 °C in winter and up to +40 °C in summer, low precipitation (270 mm), and drought. The mentioned conditions cause significant oxidative stress to all Reserve flora and fauna species. In such extreme conditions, there exist about 507 plants [1] and 71 lichen species and about 100 families of primitive mushrooms [2].
The Reserve natural conditions provide an opportunity to study the effect of geochemical anomalies on the biochemical characteristics of Baskunchak flora representatives. In this respect, the comparison of the mineral composition and antioxidant status related to three systematic groups of flora, i.e., lichens, mushrooms and vascular plants, and the differences in metabolism intensity, life span duration and nutrition are expectedly interesting. Among the mentioned organisms, Artemisia species are the most attractive due to drought and salinity tolerance and the ability to accumulate significant amounts of essential oils, which are important components of natural antioxidants [3]. Among 13 identified Artemisia species at the Reserve, perennial Artemisia lerchiana Web is the most abundant, forming broad wormwood—fescue-feather grass communities [4]. Among lichens, crustose forms dominate and are mainly confined to stony substrates. The exception is represented by the epilithic lichen Diploschistes ocellatus (Vill.) Norman found both in limestones and soils. Lichens are poikilohydric organisms absorbing the essential nutrients for growth and development mainly from the atmosphere, and overall, the passive nutrient absorption prevails over the active absorption. Nevertheless, they are able to accumulate chemical substances also taken from the substrate, tolerating higher concentrations than higher plants and mushrooms [5]. Higher fungi belong to the third group of organisms characterized by extremely intensive growth rates of fruiting bodies during the short periods of water availability. All nutrients required for the development and growth of the mushroom fruiting body are accumulated in mycelium. No species within the three mentioned groups of organisms inhabiting the Bogdinsko-Baskunchak territory have been previously characterized in terms of the ability to accumulate macro- and trace elements, and of the intensity of antioxidant protection against unfavorable environmental conditions.
Taking into account the mentioned phenomena, the aim of the present investigation was the evaluation of mineral and natural antioxidant accumulation in wormwood Artemisia lerchiana, lichen Diploschistes ocellatus and mushrooms Calvatia candida and Battarrea phalloides, in the conditions of Bogdinsko-Baskunchak Nature Reserve.

2. Results and Discussion

The comparison of biochemical and mineral characteristics of lichens, mushrooms and plants grown in the same habitat has never been performed previously. To reveal peculiarities of macro- and microelements accumulation and disclose typical properties of the defense systems of the chosen organisms, the Baskunchak Nature Reserve data were compared with the results of corresponding investigations carried out at Karadag Nature Reserve, situated at the Southern shore of the Crimean Peninsula. The latter area represents the territory of the paleo-volcano and shows complex geological structure with very dry hot summers and mild winters.
Among the organisms tested, only lichens (Diploschistes ocellatus), wormwood (Artemisia lerchiana) and Calvatia species were characterized previously in terms of biological activity, highlighting the interesting prospects of their utilization in pharmacology, cosmetics and medicine (Table 1). Up to date, no data regarding the biological activity of Battarrea phalloides (sandy stiltball) have been reported. Indeed, the only information available is devoted to the description and geographical distribution of Battarrea phalloides. Despite the wide habitat, including European countries, America, Africa and Australia, the mentioned mushroom may be found only episodically, which suggests the need for the special protection of this species [6,7,8].

2.1. Mineral Composition

Biological activity and level of tolerance to salinity, drought and high insulation in plants, lichens and higher mushrooms are determined by their physiological peculiarities, specific accumulation of biologically active compounds and mineral composition, which reflects both genetic features of the species and environmental biogeochemical characteristics [12,13,14]. In this respect, the mineral composition of Diploschistes ocellatus, Calvatia candida, Battarrea phalloides and Artemisia lerchiana represents a valuable parameter to compare lichens, mushrooms and plants in terms of adaptability to stress conditions (Table 2).
Notably, among the above-enumerated organisms, only D. ocellatus has been described as a natural hyperaccumulator of Ca [15], while up to date no information exists about the total elemental profile of this lichen and other species investigated. The comparative evaluation of Diploschistes ocellatus, Calvatia candida, Battarrea phalloides and Artemisia lerchiana biochemical and mineral composition indicates specific peculiarities of these organisms characterized by different nutrition features in conditions of intensive oxidative stress.
Ca-hyperaccumulation is typical in D. ocellatus and is recorded at different biogeochemical conditions: Baskunchak Nature Reserve and the Southern shore of Crimea (Ca concentrations reached 11.5% and 10.0%, respectively), despite significant differences in the availability of other elements (Figure 1).
Table 2 data indicate that Ca content in Artemisia lerchiana, Calvatia candida and Battarrea phalloides are 11.8 and 31.9 times lower, respectively, than Ca level in lichen. Lichen Ca coating in the form of Ca oxalate crystals in dry habitats can be facilitated by the abundance of Ca in the substrate [16] and is supposed to contribute to water conservation in thalli [17,18]. In this respect, Ca hyperaccumulation in D. ocellatus may be considered as a specific form of protection against active oxygen forms and UV radiation excess [19,20,21].
In living organisms, Ca is accompanied by Sr and there is a close relationship between these elements showing similar ionic radius and charge (Figure 2).
As shown in Figure 2, Ca/Sr ratio changes from 1289 in Calvatia candida to 1005 in lichen, and 179–202 in Battarrea phalloides and Artemisia lerchiana. In this respect, both absolute Ca and Sr levels (Table 2), and Ca/Sr ratios for puffball (1) and stiltball (3) (Figure 2), reveal great interspecies variability between these mushrooms.
On the contrary, the accumulation of other macro-elements (K, Mg, and P) was the lowest in D. ocellatus receiving nutrients mainly through the symbiosis with Trebouxia Puymaly [10]. Low accumulation of Na seems to be typical in D. ocellatus, residing in highly salty area (EC 105 mS m−1) while low Na concentration in Battarrea phalloides presumably reflects decreased levels of total dissolved solids in the soil at the Green Garden area (EC 25 mS m−1) (Figure 3A). Taking into account that Calvatia candida and Battarrea phalloides are saprotrophic organisms, they accumulate the highest levels of P, ranging from 4000 to 4366 mg kg−1 d.w.
Potassium and Mg were at close levels in A. lerchiana and the fruiting body of Calvatia candida, with the lowest concentration in lichen, which indirectly indicates similar nutrient sources for the former organisms compared to lichen. Contrary, among the species studied, Battarrea phalloides was the leader of Mg accumulation in the conditions of the Bogdinsko-Baskunchak Nature Reserve.
The K/Na ratio in plant tissues is often used as an indicator of an organism’s ability to maintain osmotic pressure in cells under salt uptake. This ratio was the highest in the Battarrea phalloides fruiting body (24.5), reached 6.6 in A. lerchiana and did not exceed two in Calvatia candida and D. ocellatus. A. lerchiana K/Na ratio in the vicinity of Ellton Salt Lake, in the neighboring Volgograd region, was 2.8 [22], which indicates the existence of some similar peculiarities in both salty regions. A. lerchiana is known to maintain high water levels in tissues under salt supply up to 800 мM NaCl. Its photosynthetic apparatus tolerance to insulation excess and low water potential in soil and in salty conditions has been shown to relate to the peculiarities of K and Na accumulation [4].
The comparison of the mineral composition of the organisms investigated revealed that the highest levels of Fe, Mn, Li, I and Si were recorded in D. ocellatus, while Battarrea phalloides accumulated predominantly B, Cu, Fe, Mn, Se and Zn (Figure 3B).
The ability of certain mushroom species to accumulate high levels of Se, Zn and Cu may protect them against oxidative stress caused by climate factors and heavy metals [23,24]. Mineral analysis revealed 3.8 times higher Fe concentrations in D. ocellatus at Baskunchak, compared to the corresponding data of the Crimean lichen. This phenomenon is in accordance with high Fe content in the Baskunchak environment, reflected in the well-known presence of red water in the Gorkaya River which flows into the lake.
At the same time, highly significant Fe accumulation in the fruiting body of Battarea phalloides and Artemisia lerchiana, compared to lichen, should be highlighted (Table 2, Figure 3B). Iron content in lichen is 6–35 times higher than in mushrooms and 11 times higher than in A. lerchiana. Higher levels of certain metals in D. ocellatus, compared to A. lerchiana and mushrooms (Figure 3C), relate to the ability of epigeic lichens, grown in substrates with high metals content, to accumulate them at higher concentration than in the substrate [25,26,27], and the precipitation phenomenon of dust containing lithospheric elements, such as Fe at the thallus surface, with their subsequent assimilation. Fe accumulation in fruiting bodies of Battarrea phalloides and Calvatia candida is a good example of wide species differences in the ability to accumulate Fe.
Compared to Crimea, at Bogdinsko-Baskunchak Nature Reserve higher accumulation of iodine (by 12 times), Li (3.6 times), Co (4.3 times) and Cu (almost twice) was recorded in Diploschistes ocellatus. The detected differences in elements accumulation reflect biogeochemical anomalies of the regions investigated and lichen genetic peculiarities. At the same time, the phenomenon of Cu hyperaccumulation in Battarea phalloides has been recorded for the first time in the present work (Table 2). In general, the latter mushroom species proved to be a powerful hyperaccumulator not only of Cu, but of B, Mn, Zn and Se. The latter phenomenon is of special importance because high soil salinity (such as that at the territory of Bogdinsko-Baskunchak Nature Reserve) reportedly inhibits the accumulation of Se [28].
Antioxidant properties of Se may be highly valuable for Calvatia candida and Battarrea phalloides grown in conditions of oxidant stress. The ability of Se hyperaccumulation is typical only of several mushroom species [24]. The present results indicate that Calvatia candida and Battarrea phalloides at the territory of Baskunchak Nature Reserve accumulated 2–25 times higher Se than lichen and 7–77 times higher than A. lerchiana (Table 2). Interestingly, high levels of Se in the Battarrea phalloides fruiting body were recorded both at the Bogdinsko-Baskunchak Nature Reserve in Astrakhan region and at Karadag in Crimea.
At the same time, A. lerchiana demonstrated increased levels of B and Mn compared to D. ocellatus and Calvatia candida data. In the conditions of Baskunchak Nature Reserve, Fe/Mn ratio varied from 174 in D. ocellatus to 16 and 13.4 in the fruiting bodies of Calvatia candida and Battarrea phalloides, respectively, and 7.7 in A. lerchiana. Mn is an essential element for all living organisms, participating in photosynthesis, respiration, free radicals scavenging, protection from pathogens and hormonal signaling [29].
Regardless of the growing area, lichen is characterized by high levels of Ca, Fe, Al, Mg, which relates either to the geochemical peculiarities of the two regions investigated or to these elements’ assimilation in thallus consequent to their air transfer from the soil surface through dust. Indeed, dust storms are typical in summer in the Astrakhan region. High levels of Al and Mg in lichens were recorded in regions rich with dolomites and lime substrates [30]. Significant amount of metals causing damage to vascular plants, is present in lichens in non-soluble forms (as oxalates), which results in physiological deactivation of these metals [31]. Indeed, Fe is deposited in the cell wall intercellular spaces of mycobiont [25].
The comparison between lichen mineral composition at Bogdinsko-Baskunchak Nature Reserve and at the Southern Crimean shore indirectly arose the insignificant differences in As, Ca, K, Na, P, B, Mo, Se accumulation reflecting both similarities of biochemical characteristics and genetic peculiarities of the species (Figure 2). The accumulation levels of mineral elements in different lichens may significantly differ and this characteristic may be used for species distinction [32]. On the other hand, at the territory of the Baskunchak Nature Reserve the high concentration of Al, Cd, Cr, Co, Fe, I, Li in lichens is predominantly determined by wind, as it is known that except for the substrate, additional Al and Fe source relates to dust precipitation on lichen thallus [33].
Plants are able to accumulate heavy metal cations, absorbing them also from air and atmospheric precipitations, but the highest accumulation ability is typical of lichens. In conditions of background heavy metal concentrations in air, their mean concentrations in lichens are usually higher than in the ground part of higher plants [34]. The comparison between A. lerchiana mineral composition from the Baskunchak Nature Reserve and the Karadag paleo-volcano territory highlights the preferential accumulation of most elements in Karadag plants, which reflects the long-term effect of the volcanic activity at Karadag (Figure 4). Indeed, high levels of Li, B and Se in the environment as a result of volcanic activity were recorded [35,36], even at Karadag Nature Reserve [37]. On the contrary, Cd, Pb and Sr levels in A. lerchiana in the vicinity of Baskunchak Lake were significantly higher than the corresponding values recorded in Karadag plants.
Overall, among the species studied, D. ocellatus was the leader in the accumulation of Al, As and the heavy metals Cr, Ni, Pb, Sr and V. The ability of Pb hyperaccumulation in Diploschistes species without showing harmful effect relates to cell protection mechanism from the toxic effect of this element. Due to increased synthesis of oxalates, Pb precipitates as insoluble salts which stimulates its high accumulation and exclusion from the metabolism, as previously shown in Diploschistes muscorum [38,39]. Among the mushrooms investigated, Battarrea phalloides demonstrated an unusually high ability to accumulate Sr, Ni, Cr, As and V.

2.2. Antioxidants

Stress is known to stimulate the formation of active oxygen forms and promote the biosynthesis of natural antioxidants. Among the latter, polyphenols occupy the leading position, indicating to a large extent the adaptive capacity of plants, lichens, and mushrooms [4,40,41,42]. Difficulties in the evaluation of the total antioxidant activity and polyphenol content include the choice of methods allowing for the maximum extraction of active components, significant effect of biogeochemical conditions and plant phenological phase. All these factors represent issues to manage for obtaining optimal results and their comparison with the published data. The results of the present investigation related to D. ocellatus demonstrated that the utilization of 70% ethanol using short-term heating is the most effective method for polyphenol (TP) extraction (Figure 5).
The efficiency of this extraction is determined by the short duration, quick deactivation of enzymes at 80 °C, which prevents polyphenols destruction, stable at high temperature [43], and low toxicity of ethanol compared to methanol. In this respect, it is interesting to indicate that polyphenol content in Calvatia candida recorded in the present work was 10 times higher than the previously reported values in conditions of prolonged extraction (24 h) at room temperature [41], though such differences are also connected with different levels of oxidative stress.
The results obtained in selected conditions indicate that A. lerchiana is characterized by the highest total antioxidant activity (AOA) and polyphenol content (Table 3).
Indeed, A. lerchiana AOA was 32 times higher than the AOA of lichen and mushrooms, while A. lerchiana polyphenol content was double compared to the values detected in Calvatia candida and D. ocellatus. Despite the different environmental conditions, these parameters did not significantly differ within both D. ocellatus samples gathered at the Baskunchak Nature Reserve and the Southern Crimean shore and A. lerchiana. The high values of A. lerchiana AOA may be also connected with high levels of essential oils [3,4]. Notably, in the list of the investigated organisms, Battarrea phalloides demonstrated the lowest antioxidant status, which was partly compensated by unusually high levels of Se accumulation. Indeed, Se is known to be another natural antioxidant capable of protecting plants from different forms of oxidant stress, caused by biotic and abiotic factors [12].
This trace element is not essential for plants, though its accumulation levels are determined both by biogeochemical peculiarities of the territory and genetic characteristics [44]. In his review, Falandysz [24] indicated several hyperaccumulators of Se among edible and toxic mushrooms (Boletus, Amanita, etc). The ability of Calvatia candida to accumulate high Se levels has also been demonstrated in this work. On the contrary, we have recorded for the first time a powerful Se hyperaccumulation in the Battarrea phalloides fruiting body. Se concentrations in D. ocellatus and A. lerchiana did not significantly differ between Baskunchak and Crimea, which indirectly indicates similar bio-accessibility of soil Se and aerosol transfer of this element. Nevertheless, Se soil bio-accessibility at Baskunchak Nature Reserve needs special investigations due to extremely high salinity predominantly caused by magnesium chloride (90% MgCl2, 9% MgSO4, 1% NaCl), gypsum deposits and water deficiency. Sulfur as a Se analog is known to prevent Se accumulation in plants [28,45].

2.3. Proline

The amino acid proline is essential for plants under stress conditions. In addition to being an excellent osmoregulator, proline also acts as a metal chelator, antioxidant and signaling molecule. In stress conditions, proline biosynthesis is enhanced to maintain osmotic balance. It stabilizes membranes, avoiding electrolytes leakage, normalizing the levels of oxygen active forms thus preventing oxidant stress. Proline supplementation is known to increase plant tolerance to stress factors and stabilize subcellular structures (membranes and proteins) via scavenging free radicals. In many plants, proline accumulation level correlates with stress resistance [46,47].
Table 3 data indicate that at the territory of Bogdinsko-Baskunchak Nature Reserve, A. lerchiana accumulated five times more proline than D. ocellatus and mushrooms. This phenomenon is determined to a large extent by the peculiarities of the organisms’ development: A. lerchiana is characterized by long vegetation period and high salinity tolerance; D. ocellatus spends most time in quiescence, while the fruiting body of mushrooms is ephemeric and has an extremely short life. Close values of proline accumulation at Baskunchak Nature Reserve and the Southern Crimean shore indicate similarities in oxidant stress values at these territories.

2.4. Malonic dialdehyde (MDA)

Metabolic differences in proline accumulation by Diploschistes ocellatus, Calvatia candida, Battarrea phalloides and A. lerchiana are also connected with malonic dialdehyde (MDA) accumulation, reflecting the intensity of lipid peroxidation and the levels of oxidant stress (Figure 6). Indeed, the highest MDA levels were recorded in mushrooms, with the highest rate of metabolism and extremely limited duration of life cycle, and the lowest in D. ocellatus, which may relate, priority, to the possibility of development of physiological processes in wet thallus and its complete cessation in dry thallus. Taking into account that mostly lichens are quiescent, the effect of stress factors is negligible for them. MDA level in Baskunchak Artemisia lerchiana was close to that of plants grown in the vicinity of Elton Lake (Volgograd region) [22] and at the territory of Karadag Nature Reserve (Figure 6). Products of lipid peroxidation are known to change ionic channels, including calcium [48].

2.5. Carbohydrates

Monosaccharides belong to another group of osmoregulators in plants. These compounds are practically absent in the fruiting bodies of mushrooms and lichen. On the contrary, A. lerchiana was shown to accumulate up to 3.6% of monosaccharides per d.w., which indicates the high adaptability level of this plant. In the conditions of Elton Lake vicinity, A. lerchiana accumulated only 2% monosaccharides [22].

2.6. Photosynthetic Pigments

Table 4 data provide the first information regarding chlorophyll a, b and carotene content in D. ocellatus and A. lerchiana at Bogdinsko-Baskunchak Nature Reserve. Chlorophyll content in A. lerchiana was 6.6 times higher than in lichen, while carotene content was almost 30 time lower. The results of the present investigation are in accordance with Shmakova and Markovskaya report [49], who investigated plants and lichens at the territory of Spitsbergen, showing the increase in chlorophyll and carotene content as well as chlorophyll/carotene ratio, with the improvement of organism organization with relative stability of chlorophyll a/b ratio. The latter parameter did not significantly differ between D. ocellatus and A. lerchiana (2.2), while chlorophyll/carotene ratio reached 7 and 30.7 in A. lechriana and D. ocellatus, respectively. Notably, in the conditions of Bogdinsko-Baskunchak Nature Reserve, A. lerchiana accumulated predominantly chlorophyll b, while in the vicinity of Elton Lake chlorophyll a prevailed in wormwood leaves [22].
Lichens are symbiotrophic organisms, whereas photosynthesis is achieved by algae and/or cyanobacteria. In laboratory experiments, the photobiont Trebouxia sp. TR9 under salinity stress conditions decreased chlorophyll content with salt concentration increase [50]. As lichens are poikilohydric organisms, high photosynthesis efficiency may take place only in conditions of optimal thallus water saturation [51]. Diploschistes species inhabit arid habitats [20], thus their metabolic activity covers a very short time span, and active metabolism processes coincide with the rainy season. Laboratory experiments with D. diacapsis from arid habitats revealed a close relationship between photosynthesis, respiration intensity and chlorophyll content in water saturated thallus [52]. While many lichen species demonstrate photosynthesis decrease in conditions of high thallus water saturation, D. muscorum photosynthesis rate remains close to the maximum even in conditions of extremely high thallus water saturation [53]. D. scruposus demonstrates not significant photosynthesis depression in the latter conditions [53]. It is supposed that such reaction of Diploschistes representatives relates to the presence of hydrophobic proteins in micobiont and interactions between the symbionts [53,54].
The scant data regarding photosynthetic pigment accumulation in lichens and wormwoods in conditions of intensive oxidant stress, such as soil salinity, entails the necessity of further investigations at the territory of Bogdinsko-Baskunchak Nature Reserve.

3. Material and Methods

Twelve samples of lichen Diploschistes ocellatus, nine of puffball Calvatia candida fruiting bodies, 12 of Battarrea phalloides and 18 of wormwood Artemisia lerchiana were gathered at the Bogdinsko-Baskunchak Nature Reserve territory in Russia (Figure 7A) in May 2021 and 2022. Lichen thalli were collected at the soil surface.
The Crimean samples of Artemisia lerchiana (Karadag Nature Reserve), Battarrea phalloides, Calvatia candida (Karadag Nature Reserve), and Diploschistes ocellatus (Novy Svet settlement) were compared in this investigation (Figure 7B).
Gathered samples were ground and dried at room temperature and homogenized.

3.1. Mineral Composition

The determination of 25 elements (Al, As, B, Ca, Cd, Co, Cr, Cu, Fe, I, K, Li, Mg, Mn, Mo, Na, Ni, P, Pb, Se, Si, Sn, Sr, V, and Zn) was performed on dried homogenized samples using ICP-MS on quadruple mass-spectrometer Nexion 300D (Perkin Elmer Inc., Shelton, CT, USA), according to Golubkina et al. [55].

3.2. Total Polyphenols (TP)

Total polyphenols were assessed in 70% ethanol extract using the Folin–Ciocalteu reagent [43]. The extraction of antioxidants was done on dry homogenized samples at 80 °C for 1 h. After cooling, adjusting the volume to 25 mL, and filtrating, 1 mL of the resulting solution was mixed with 2.5 mL of 20% Na2CO3 solution and 0.25 mL of diluted (1:1) Folin–Ciocalteu reagent in a 25 mL volumetric flask, and the volume was brought to 25 mL with distilled water. One hour later, polyphenol content was determined based on the absorption of the reaction mixture at 730 nm. As an external standard, 0.02% gallic acid was used. The results were expressed as mg of Gallic Acid Equivalent per g of dry weight (mg GAE g−1 d.w).

3.3. Antioxidant Activity (AOA)

The antioxidant activity of samples was determined using a redox titration of 0.01 N KMnO4 solution with ethanolic extracts of dry samples, produced as described in the Section 3.2 [43]. Gallic acid was used as an external standard. The values were expressed in mg Gallic Acid Equivalents (mg GAE g−1 d.w.).

3.4. Proline

Proline concentration was determined according to Quertani et al. [46], with slight modifications. About 50 mg of dry homogenized Artemisia leaves or 100 mg of dried lichen/mushrooms powder were grinded with 10 mL of 3% sulfur salicylic acid in a mortar. After filtration, 1 mL of the resulting filtrate was mixed with 2 mL of ninhydrin reagent and 2 mL of acetic acid and then heated at 95 °C for 1 h. Proline concentration was assessed using the absorption value of the reaction mixture at 505 nm and a calibration curve with five different proline (Kenilworth, NJ, USA, Merck) concentrations.

3.5. Malonic Dialdehyde (MDA)

Lipid peroxidation was measured by tracing malonic dialdehyde content using thiobarbituric acid method as described by Heath and Parker [56], with a small modification. About 0.1 g of dried sample were mixed with 10 mL of 0.5% thiobarbituric acid solution and heated at 95 °C for half an hour. After cooling, the mixture was filtered and the filtrate was subjected to measurements by a spectrophotometer Unico 2804 UV (Suite E Dayton, NJ, USA). MDA content was calculated using the absorption value at 232 nm and the extinction value of 155 mM cm−1.

3.6. Carbohydrates

The monosaccharides were determined using the ferricyanide colorimetric method, based on the reaction of potassium ferricyanide with monosaccharides and fructose as an external standard [57]. The total sugars were analogically assessed after acidic hydrolysis of water extracts with 20% hydrochloric acid. The results were expressed in % per d.w.

3.7. Photosynthetic Pigments

Photosynthetic pigments accumulation was evaluated by spectrophotometer (Unico 2804 UV, USA) using 96% ethanolic extracts of dry samples according to Lichtenthaler [58]. The following equations were used to calculate chlorophyll and carotene concentrations:
Ch-a = 13.36 A664 − 5.19 A649;
Ch-b = 27.43 A649 − 8.12 A664;
C c = (1000 A470 − 2.13 Ch-a − 87.63 Ch-b)/209;
where A = Absorbance, Ch-a = Chlorophyll a, Ch-b = Chlorophyll b and
C c = Carotene.

3.8. Statistical Analysis

The data were processed by the analysis of variance and mean separations were performed through the Duncan’s multiple range test, with reference to 0.05 probability level using SPSS software version 27.

4. Conclusions

The results of the first biochemical and mineral characterization ever performed of organisms from different systematic groups, such as lichens, mushrooms and plants, in conditions of increased salinity at the Baskunchak Nature Reserve (Russia) revealed the peculiarities of mineral composition and antioxidant status. Diploschistes ocellatus displayed hyperaccumulation of Ca, Al, Cr, Sr, Fe, Si, with minimum levels of K, Na, P, Cd, Cu and Zn; in the fruiting body of Calvatia candida, intensive accumulation of Se, Na, P and Cd was recorded and extremely low levels of Al, As, Cr, Ni, Pb, V, Co, Li and Mo, and the highest MDA accumulation; in the fruiting body of Battarrea phalloides, hyperaccumulation of Fe, Mn, Se, Zn and Sr and the lowest accumulation of Na was found; in A. lerchiana, the highest antioxidant activity, proline and monosaccharides content and high Mn and B levels were detected. Further investigations are needed to study plant responses to intensive oxidant stress in the conditions of the Baskunchak Nature Reserve.

Author Contributions

Conceptualization: N.G., V.Z., A.S. and G.C.; formal analysis, V.Z., A.T. and O.C.M.; investigation, N.G., T.T., V.L., H.L. and N.P., methodology, A.S., O.C.M. and A.T.; validation, N.G., A.S., V.S. and G.C.; draft manuscript writing, N.G., T.T., V.S. and G.C.; manuscript revision and final editing, N.G., T.T., A.S. and G.C. All authors have read and agreed to the published version of the manuscript.

Funding

This research did not receive any grants from public, commercial, or not-for-profit agencies and was carried out according to the State assignment №121032300023-7 “Investigation of peculiarities of terrestrial ecosystems structure and dynamics in different ecological zones” (Karadag Nature Reserve) and the scientific project of the state task of the Lomonosov Moscow State University No 121032300081-7.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Volobaeva, O.V. Bogdinsko-Baskunchak Nature Reserve Flora. Ph.D. Thesis, Bashkir State University, Ufa, Russia, 2021. (In Russian). [Google Scholar]
  2. Chuicov, J.S. Bogdinsko-Baskunchak Nature Reserve Complex and Its Protection; OOO CNTEP: Astrakhan, Russia, 1998. (In Russian) [Google Scholar]
  3. Golubkina, N.; Logvinenko, L.; Molchanova, A.; Caruso, G. Genetic and Environmental Influence on Macro- and Micro-elements Accumulation in Plants of Artemisia Species. In Plant Micronutrients: Deficiency and Toxicity Management; Aftab, T., Ed.; Chapter 17; Springer: Berlin, Germany, 2020. [Google Scholar]
  4. Orlova, J.V. Ecophysiological Characteristics of Artemisia lerchiana Web in conditions of Low Volga region. Ph.D. Thesis, Moscow, Russia, 2009. (In Russian). [Google Scholar]
  5. Purvis, O.W.; Halls, S. A review of lichens in metal-enriched environments. Lichenologist 1996, 28, 571–601. [Google Scholar] [CrossRef]
  6. Evans, S. Conservation corner. Field Mycol. 2001, 2, 116–117. [Google Scholar] [CrossRef]
  7. Marren, P. Stinkhorns, earthstars and fungal flowers: The strange world gasteromycete fungi. Br. Wildl. 1995, 6, 366–376. [Google Scholar]
  8. Gargano, M.L.; Venturella, G.; Ferraro, V. Is Battarrea phalloides really an endangered species? Plant Biosyst.-Int. J. Plant Biol. (Off. J. Soc. Bot. Ital.) 2020, 155, 759–762. [Google Scholar]
  9. Hedawoo, G.B. Calvatia species: Wild edible puff balls from Armavati region (M.S.). Plantae Sci. 2020, 3, 30–34. [Google Scholar] [CrossRef]
  10. Fernández-Brime, S.; Llimona, X.; Lutzoni, F.; Gaya, E. Phylogenetic study of Diploschistes (lichen-forming Ascomycota: Ostropales: Graphidaceae), based on morphological, chemical, and molecular data. Taxon 2013, 62, 267–280. [Google Scholar] [CrossRef] [Green Version]
  11. Mendili, M.; Bannour, M.; Araújo, M.E.M.; Aschi-Smit, S.; Seaward, M.R.D.; Khadhria, A. Secondary metabolites and antioxidant capacity of the Tunisian lichen Diploschistes ocellatus (Ascomycot a). Int.J. Med. Mushrooms 2019, 19, 817–823. [Google Scholar] [CrossRef] [PubMed]
  12. Golubkina, N.A.; Kharchenko, V.A.; Caruso, G. Selenium: Prospects of functional food production with high antioxidant activity Reference Series in Phyto-chemistry. In Plant Antioxidants and Health; Ekiert, H., Ramawat, K.G., Arora, J., Eds.; Springer: Berlin, Germany, 2021. [Google Scholar] [CrossRef]
  13. Kalač, P. A review of chemical composition and nutritional value of wild-growing and cultivated mushrooms. J. Sci. Food Agric. 2013, 93, 209–218. [Google Scholar] [CrossRef]
  14. Delmail, D.; Grube, M.; Parrot, D.; Cook-Moreau, J.; Boustie, J.; Labrousse, P.; Tomasi, S. Halotolerance in lichens: Symbiotic coalition against salt stress. In Ecophysiology and Responses of Plants under Salt Stress; Ahmad, P., Ed.; Springer Science + Business Media, LLC: New York, NY, USA, 2013; p. 115. [Google Scholar] [CrossRef]
  15. Piterance, A.V. Diploschistaceae family. Key of lichens of the USSR. Calcium–Gialectic 1975, 3, 45–53. (In Russian) [Google Scholar]
  16. Weber, W.A. Environmental modifications and the taxonomy of the crustose lichens. Svensk. Botanisk Tidskrift. 1962, 56, 293–333. [Google Scholar]
  17. Wadsten, T.; Moberg, R. Calcium oxalate hydrates on the surface of lichens. Lichenologist 1985, 17, 239–245. [Google Scholar] [CrossRef]
  18. Ručová, D.; Đorđević, T.; Baláž, M.; Weidinger, M.; Lang, I.; Gajdoš, A.; Goga, M.l. Investigation of calcium forms in lichens from Travertine sites. Plants 2022, 11, 620. [Google Scholar] [CrossRef] [PubMed]
  19. Cavigia, A.M.; Modenesi, P. Oxidative stress and ascorbic contents in Parmotrema reticulatum and Parmelia sulcata thalli. Lichenologist 1999, 31, 105–110. [Google Scholar] [CrossRef]
  20. Modenesi, P.; Piana, M.; Giordani, P.; Tafanelli, A.; Bartoli, A. Calcium oxalate and medullary architecture in Xanthomaculina convolute. Lichenologist 2000, 32, 505–512. [Google Scholar] [CrossRef]
  21. Modenesi, P.; Bombardi, V.; Giordani, P.; Brunialti, G.; Carallo, A. Dissolution of weddellite, calcium oxalate dehydrate, in Pyxine subcinerea. Lichenologist 2001, 33, 261–266. [Google Scholar] [CrossRef]
  22. Rosentsvet, O.A.; Nesterov, V.N.; Bogdanova, E.C.; Tabalenkova, G.N.; Zakhogy, I.G.; Popov, A.V. Effect of Ellton salinity soils on functional conditions of Artemisia representatives. Izv. RAS Biol. Ser. 2019, 3, 312–320. (In Russian) [Google Scholar]
  23. Golubkina, N.A.; Mironov, J.V. Element composition of mushrooms in contrasting anthropogenic loading. Geochem. Int. 2018, 56, 1263–1275. [Google Scholar]
  24. Falandysz, J. Selenium in edible mushrooms. J. Environ. Sci. Health Part C 2008, 26, 256–299. [Google Scholar] [CrossRef] [Green Version]
  25. Nöeske, O.; Läuchli, A.; Lange, O.L.; Vieweg, G.H.; Ziegler, H. Konzentration und Lokalisierung von Schwermetallen in Flechten der Erzschlackenhalden des Harzes. Vortr. Gesamtgeb. Ber. Dtsch. Bot. Ges. 1970, 4, 67–79. [Google Scholar]
  26. Lawrey, J.D.; Rudolph, E.D. Lichen accumulation of some heavy metals from acids surface substrates of coal mine ecosystems in southeastern Ohio. Ohio J. Sci. 1975, 75, 113–117. [Google Scholar]
  27. Purvis, O.W.; Elix, J.A.; Gaul, K.L. The occurrence of copper-norstictic acid in lichens from cupriferous substrata. Lichenologist 1990, 22, 345–354. [Google Scholar] [CrossRef]
  28. Mikkelsen, R.L.; Page, A.L.; Haghnia, G.H. Effect of salinity and its composition on the accumulation of selenium by alfalfa. Plant Soil 1988, 107, 63–67. [Google Scholar] [CrossRef]
  29. Alejandro, S.; Holler, S.; Meier, B.; Peiter, E. Manganese in plants: From acquisition to subcellular allocation. Front. Plant Sci. 2020, 11, 300. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  30. Corapi, A.; Gallo, L.; Nicolardi, V.; Lucadamo, L.; Loppi, S. Temporal trends of element concentrations and ecophysiological parametrsin in the lichen Pseudevernia furfuracea transplanted in and around in industrial area S Italy. Environ. Monit. Assess. 2014, 186, 3149–3164. [Google Scholar] [CrossRef]
  31. Byazrov, L.G. Lichens in Ecological Monitoring; Nauchny Mir: Moscow, Russia, 2002; 336p. (In Russian) [Google Scholar]
  32. Bennett, J.P. Discrimination of lichen genera and species using element concentrations. Lichenologist 2008, 40, 135–151. [Google Scholar] [CrossRef]
  33. Nash, T.H., III. Nutrients, elemental accumulation, and mineral cycling. In Lichen Biology; Cambridge University Press: Cambridge, UK, 2010; pp. 236–253. [Google Scholar] [CrossRef]
  34. Insarova, I.D. Heavy metals effect on lichens. Problems of ecological monitoring and ecosystems modeling. Leningrad 1983, 6, 101–113. (In Russian) [Google Scholar]
  35. Benson, T.R.; Coble, M.A.; Rytuba, J.J.; Mahood, G.A. Lithium enrichment in intracontinental rhyolite magmas leads to Li deposits in caldera basins. Nat. Commun. 2017, 8, 270. [Google Scholar] [CrossRef] [PubMed]
  36. Winkel, L.H.E.; Vriens, B.; Jones, G.D.; Schneider, L.S.; Pilon-Smits, E.; Bañuelos, G.S. Selenium cycling across soil-plant-atmosphere interfaces: A critical review. Nutrients 2015, 7, 4199–4239. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  37. Golubkina, N.; Lapchenko, V.; Lapchenko, H.; Zuev, A.; Caruso, G. Seasonal dynamics of groundwater mineral composition at the territory at the Crimean paleovolcano. Bull. Nikita Bot. Gard. 2022, 142, 129–135. [Google Scholar]
  38. Osyczka, P.; Latkowska, E.; Rola, K. Metabolic processes involved with sugar alcohol and secondary metabolite production in the hyperaccumulator lichen Diploschistes muscorum reveal its complex adaptation strategy against heavy-metal stress. Fungal Biol. 2021, 125, 999–1008. [Google Scholar] [CrossRef]
  39. Sarret, G.; Manceau, A.; Cuny, D.; van Haluwyn, C.; Déruelle, S.; Hazemann, J.-L.; Soldo, Y.; Eybert-Bŭrard, L.; Menthonnex, J.-J. Mechanisms of lichen resistance to metallic pollution. Environ. Sci. Technol. 1998, 32, 3325–3330. [Google Scholar] [CrossRef]
  40. Kosanić, M.; Ranković, B. Studies on antioxidant properties of lichen secondary metabolites. In Lichen Secondary Metabolites; Ranković, B., Ed.; Springer: New York, NY, USA, 2019. [Google Scholar] [CrossRef]
  41. Novaković, A.R.; Karaman, M.A.; Matavulj, M.N.; Pejin, B.M.; Belović, M.M.; Radusin, T.I.; Ilić, N.M. An insight into in vitro bioactivity of wild-growing puffball species Lycoperdon perlatum (Pers) 1796. Food Feed Res. 2015, 42, 51–58. [Google Scholar] [CrossRef] [Green Version]
  42. Román, M.P.G.; Mantilla, N.B.; Flórez, S.A.C.; De Mandal, S.; Passari, A.K.; Ruiz-Villáfan, B.; Rodríguez-Sanoja, R.; Sánchez, S. Chapter Antimicrobial and antioxidant potential of wild edible mushrooms. In An Introduction to Mushroom; Intechopen: London, UK, 2020. [Google Scholar] [CrossRef] [Green Version]
  43. Golubkina, N.A.; Kekina, H.G.; Molchanova, A.V.; Antoshkina, M.S.; Nadezhkin, S.; Soldatenko, A.V. Plants Antioxidants and Methods of Their Determination; Infra-M: Moscow, Russia, 2020; (In Russian). [Google Scholar] [CrossRef]
  44. Gupta, M.; Gupta, S. An overview of selenium uptake, metabolism and toxicity in plants. Front. Plant Sci. 2017, 7, 2074. [Google Scholar] [CrossRef] [Green Version]
  45. Lanza, M.G.D.B.; dos Reis, A.R. Roles of selenium in mineral plant nutrition: ROS scavenging responses against abiotic stresses. Plant Physiol. Biochem. 2021, 164, 27–43. [Google Scholar] [CrossRef]
  46. Ouertani, R.N.; Abid, G.; Karmous, C.; Chikha, M.B.; Boudaya, O.; Mahmoudi, H.; Mejri, S.; Jansen, K.; Ghorbel, A. Evaluating the contribution of osmotic and oxidative stress components on barley growth under salt stress. AoB Plants 2021, 13, plab034. [Google Scholar] [CrossRef] [PubMed]
  47. Hayat, S.; Hayat, Q.; Alyemeni, M.N.; Wani, A.S.; Pichtel, J.; Ahmad, A. Role of proline under changing environments. A review. Plant Signal Behav. 2012, 7, 1456–1466. [Google Scholar] [CrossRef] [Green Version]
  48. Schmidt, R.; Kunkiwska, A.B.; Schippers, J.H.M. Role of reactive oxygen species during cell expansion in leaves. Plant Physiol. 2016, 172, 2098–2106. [Google Scholar] [CrossRef] [Green Version]
  49. Shmakova, N.Y.; Markovskaya, E.F. Photosynthetic pigments of plants and lichens in Arctic tundra of west Spitsbergen. Rus. J. Plant Physiol. 2010, 57, 764–769. [Google Scholar] [CrossRef]
  50. Hinojosa-Vidal, E.; Marco, F.; Martínez_Alberola, F.; Escaray, F.J.; García-Breijo, F.J.; Reid-Armińana, J.; Carrasco, P.; Barreno, E. Characterization of the Responses to Saline Stress in the Symbiotic Green Microalga Treboixia sp. TR9. Planta 2018, 1, 14. [Google Scholar] [CrossRef]
  51. Green, T.G.A.; Nash, T.H., III; Lange, O.L. Physiological ecology of carbon dioxide exchange. In Lichen Biology; Chapter 9; Nash, T.H., III, Ed.; Cambridge University Press: Cambridge, UK, 2008; pp. 152–181. [Google Scholar] [CrossRef]
  52. Pintado, A.; Sancho, L.G.; Green, T.G.A.; Blanquer, J.M.; Lázaro, R. Function ecology of the biological soil crust in semiarid SE Spain: Sun and shade populations of Diploshistes diacapsis (Ach.) Lumbisch. Lichenologist 2005, 37, 425–432. [Google Scholar] [CrossRef] [Green Version]
  53. Lange, O.L.; Green, T.G.A.; Reichenberger, H.; Chaidir, C. Do secondary substances in the thallus of a lichen promote CO2 diffusion and prevent depression of net photosynthesis at high water content? Oecologia 1997, 112, 1–3. [Google Scholar] [CrossRef] [PubMed]
  54. Lange, O.L.; Green, T.G.A.; Reichenberger, H. The response of lichen photosynthesis to external CO2 concentration and its interaction with thallus water-status. J. Plant Physiol. 1999, 154, 157–166. [Google Scholar] [CrossRef]
  55. Golubkina, N.; Antoshkina, M.; Bondareva, L.; Sekara, A.; Campagna, E.; Caruso, G. Effect of foliar application of sodium selenate on mineral relationships in Brassicaceae crops. Horticulturae 2023, 9, 535. [Google Scholar] [CrossRef]
  56. Heath, R.L.; Parker, L. Photoperoxidation in isolated chloroplasts. I. Kinetics and stoichiometry of fatty acid peroxidation. Arch. Biochem. Biophys. 1968, 125, 189–198. [Google Scholar] [CrossRef] [PubMed]
  57. Swamy, P.M. Laboratory Manual on Biotechnology; Rastogi: New Delhi, Rastogi Publications, New Delhi, India, 2008; pp. 101–104. [Google Scholar]
  58. Lichtenthaler, H.K. Chlorophylls and carotenoids: Pigments of photosynthetic bio-membranes. Methods Enzymol. 1987, 148, 350–382. [Google Scholar]
Figure 1. Differences in macro- and microelements accumulation in lichen Diploschistes ocellatus at the territory of Baskunchak Nature Reserve and the Southern Crimean shore; (*)—lack of statistically significant differences between Baskunchak/Crimea data.
Figure 1. Differences in macro- and microelements accumulation in lichen Diploschistes ocellatus at the territory of Baskunchak Nature Reserve and the Southern Crimean shore; (*)—lack of statistically significant differences between Baskunchak/Crimea data.
Plants 12 02530 g001
Figure 2. Correlation between Ca and Sr accumulation in Calvatia candida (1), Artemisia lerchiana (2) Battarrea phalloides (3) and Diploschistes ocellatus (4) at the Bogdinsko-Baskunchan Nature Reserve.
Figure 2. Correlation between Ca and Sr accumulation in Calvatia candida (1), Artemisia lerchiana (2) Battarrea phalloides (3) and Diploschistes ocellatus (4) at the Bogdinsko-Baskunchan Nature Reserve.
Plants 12 02530 g002
Figure 3. Accumulation of macro- (A), microelements (B), and As, Al and heavy metals (C) in lichen Diploschistes ocellatus, mushrooms Calvatia candida and Battarrea phylloides, and plant Artemisia lerchiana at the territory of Bogdinsko-Baskunchak Nature Reserve. For each element, values with the same letters do not differ statistically according to Duncan test at p < 0.05.
Figure 3. Accumulation of macro- (A), microelements (B), and As, Al and heavy metals (C) in lichen Diploschistes ocellatus, mushrooms Calvatia candida and Battarrea phylloides, and plant Artemisia lerchiana at the territory of Bogdinsko-Baskunchak Nature Reserve. For each element, values with the same letters do not differ statistically according to Duncan test at p < 0.05.
Plants 12 02530 g003
Figure 4. Differences in macro- and microelement accumulation in Artemisia lerchiana at Baskunchak and Karadag Nature Reserves (Crimea). (*): lack of statistically significant differences between Baskunchak/Crimea data.
Figure 4. Differences in macro- and microelement accumulation in Artemisia lerchiana at Baskunchak and Karadag Nature Reserves (Crimea). (*): lack of statistically significant differences between Baskunchak/Crimea data.
Plants 12 02530 g004
Figure 5. Effect of extraction conditions on polyphenol (TP) content in Diploschistes ocellatus (*—80 °C, 1 h; in other cases, 60 °C, 1 h). Values with the same letters do not differ statistically according to Duncan test at p < 0.05.
Figure 5. Effect of extraction conditions on polyphenol (TP) content in Diploschistes ocellatus (*—80 °C, 1 h; in other cases, 60 °C, 1 h). Values with the same letters do not differ statistically according to Duncan test at p < 0.05.
Plants 12 02530 g005
Figure 6. Malonic dialdehyde content in Diploschistes ocellatus, Calvatia candida, Battarrea phalloides and Artemisia lerchiana in conditions of Baskunchak Nature Reserve and Crimea. The standard error is shown. Values with the same letters do not differ statistically according to Duncan test at p < 0.05.
Figure 6. Malonic dialdehyde content in Diploschistes ocellatus, Calvatia candida, Battarrea phalloides and Artemisia lerchiana in conditions of Baskunchak Nature Reserve and Crimea. The standard error is shown. Values with the same letters do not differ statistically according to Duncan test at p < 0.05.
Plants 12 02530 g006
Figure 7. Sampling sites of lichens Diploschistes ocellatus (1), mushrooms Calvatia candida (Rostk.) Hollós (2) and Battarrea phalloides (Dicks.) Pers (3), and wormwood Artemisia lerchiana (4), at the territory of Bogdinsko-Baskunchak Nature Reserve (A) and at the Crimean Southern shore (B).
Figure 7. Sampling sites of lichens Diploschistes ocellatus (1), mushrooms Calvatia candida (Rostk.) Hollós (2) and Battarrea phalloides (Dicks.) Pers (3), and wormwood Artemisia lerchiana (4), at the territory of Bogdinsko-Baskunchak Nature Reserve (A) and at the Crimean Southern shore (B).
Plants 12 02530 g007
Table 1. Biological activity of Calvatia species, Diploschistes ocellatus and Artemisia lerchiana.
Table 1. Biological activity of Calvatia species, Diploschistes ocellatus and Artemisia lerchiana.
CharacteristicsBiological EffectBiologically Active Compounds
Calvatia speciesTerrestrial saprophytesAntibacterial, antiviral, antitumor and wound healing properties [9]Calvatin and calvatic acid
Diploschistes ocellatusSymbiotic organism of fungi and algae Trebouxia, calcephitis
[10]
Photo-protective, anti-microbial to gram-positive and gram-negative bacteria, anti-fungal to Enterococcus faecalis [11] Polyphenols, flavonoids
Artemisia lerchianaHaloxerophitis with high tolerance to water deficiency and soil salinity Allopathic, fungicidal, bactericidal and antioxidant [4]Essential oil (camphor derivatives)
Table 2. Mineral composition of Diploschistes ocellatus, Calvatia candida, Battarrea phalloides and Artemisia lerchiana at Baskunchak Nature Reserve and Karadag Nature Reserve (mg Kg−1 d.w.).
Table 2. Mineral composition of Diploschistes ocellatus, Calvatia candida, Battarrea phalloides and Artemisia lerchiana at Baskunchak Nature Reserve and Karadag Nature Reserve (mg Kg−1 d.w.).
ElementDiplishistes ocellatusBattarrea phalloidesCalvatia candidaArtemisia lerchiana
BaskunchakCrimeaBaskunchakCrimeaBaskunchakCrimeaBaskunchakCrimea
Ca114,617 ± 11,210 a100,656 ± 10,006 a10,014 ± 1000 c1020 ± 100 e 3596 ± 317 d850 ± 82 e9728 ± 934 c13,600 ± 133 b
K1389 ± 129 e987 ± 96 f8044 ± 776 d 34,406 ± 3101 a22,543 ± 2052 c26,754 ± 2588 bc22,306 ± 2180 c28,195 ± 2800 b
Mg934 ± 93 d352 ± 32 f3052 ± 298 a952 ± 93 d1514 ± 148 c672 ± 67 e1815 ± 180 bc1858 ± 184 b
Na873 ± 83 c831 ± 80 c328 ± 33 e502 ± 47 d10,851 ± 1001 a11,080 ± 1000 a3357 ± 328 b2939 ± 289 b
P302 ± 27 d373 ± 33 d4366 ± 431 b8167 ± 802 a4017 ± 389 b9655 ± 925 a1938 ± 190 c2175 ± 207 c
B7.90 ± 0.68 c7.24 ± 0.69 c23.65 ± 2.20 b6.59 ± 0.62 c4.10 ± 0.40 d2.00 ± 0.20 e22.23 ± 2.11 b46.99 ± 4.7 a
Co1.23 ± 0.12 a0.28 ± 0.03 c1.04 ± 0.11 a0.20 ± 0.02 d0.07 ± 0.01 e0.02 ± 0.01 f0.25 ± 0.02 c0.64 ± 0.06 b
Cu5.18 ± 0.49 d2.80 ± 0.30 e82.14 ± 8.01 a103.00 ± 10.10 a9.96 ± 0.90 c11.21 ± 1.10 c10.17 ± 1.01 c19.64 ± 1.88 b
Fe5072 ± 489 a1347 ± 127 b837 ± 82 c267 ± 25 e145 ± 14.2 f109 ± 10 g444 ± 44 d 1542 ± 145 b
I15.05 ± 1.45 a1.23 ± 0.11 bc0.76 ± 0.07 d0.40 ± 0.04 e0.40 ± 0.04 e0.33 ± 0.03 e1.03 ± 0.09 c1.34 ± 0.12 b
Li3.50 ± 0.34 a0.96 ± 0.09 c0.65 ± 0.06 e0.49 ± 0.05 f0.08 ± 0.01 g0.07 ± 0.01 g0.89 ± 0.08 d2.36 ± 0.20 b
Mn29.20 ± 2.88 c14.00 ± 1.30 d62.46 ± 6.12 b14.50 ± 1.43 d9.09 ± 0.90 e6.59 ± 0.60 f57.48 ± 5.71 b117 ± 10 a
Mo 0.31 ± 0.03 b0.23 ± 0.02 c0.93 ± 0.09 a0.15 ± 0.01 d0.15 ± 0.01 d0.12 ± 0.01 f0.31 ± 0.03 b0.98 ± 0.09 a
Se0.25 ± 0.02 e0.15 ± 0.01 f6.14 ± 0.59 b8.13 ± 0.80 a0.59 ± 0.06 d0.85 ± 0.08 c0.08 ± 0.01 g0.29 ± 0.03 e
Si22.26 ± 2.01 c15.06 ± 1.43 c5.93 ± 0.60 f54.90 ± 5.20 a5.68 ± 0.57 f38.67 ± 3.82 b10.06 ± 1.00 e13.42 ± 1.29 d
Zn16.08 ± 1.55 g30.24 ± 3.00 ef107.00 ± 10.00 a59.30 ± 5.35 b39.19 ± 3.85 cd28.12 ± 2.80 f33.19 ± 3.30 de44.91 ± 4.38 c
Al3139 ± 301 a1086 ± 100 b193 ± 18 e126 ± 12 f99 ± 9 g59 ± 6 h346 ± 32 d721 ± 72 c
As1.41 ± 0.11 a1.48 ± 0.15 a0.90 ± 0.09 b0.28 ± 0.02 d0.04 ± 0.01 d0.02 ± 0.01 f0.20 ± 0.02 e0.70 ± 0.07 c
Cd0.06 ± 0.01 f0.30 ± 0.03 d1.20 ± 0.10 a0.63 ± 0.06 c0.84 ± 0.08 b0.53 ± 0.05 c0.12 ± 0.01 e0.08 ± 0.01 f
Cr54.46 ± 5.10 a2.33 ± 0.21 c3.39 ± 0.34 b0.69 ± 0.06 e0.67 ± 0.06 e0.28 ± 0.03 f1.10 ± 0.10 d1.98 ± 0.20 c
Ni10.90 ± 1.92 a3.35 ± 0.33 bc3.77 ± 0.35 b0.51 ± 0.05 d0.30 ± 0.03 b0.12 ± 0.01 e3.03 ± 0.30 c3.04 ± 0.30 c
Pb5.54 ± 0.52 b15.48 ± 1.47 a1.09 ± 0.10 c0.70 ± 0.07 d0.10 ± 0.01 e0.07 ± 0.01 f0.62 ± 0.06 d1.09 ± 0.11 c
Sr114.00 ± 11.00 a49.09 ± 4.78 b56.00 ± 5.20 b4.67 ± 0.05 c2.79 ± 0.30 d1.06 ± 0.10 e48.14 ± 4.80 b107.00 ± 10.00 a
V6.78 ± 0.63 b14.68 ± 1.44 a2.89 ± 0.30 c0.51 ± 0.04 d0.31 ± 0.03 e0.29 ± 0.03 e2.69 ± 0.24 c6.59 ± 0.55 b
Along each line, the values with the same letters do not differ statistically according to Duncan test at p < 0.05.
Table 3. Antioxidant status of Diploschistes ocellatus, Calvatia candida, Battarrea phalloides and Artemisia lerchiana.
Table 3. Antioxidant status of Diploschistes ocellatus, Calvatia candida, Battarrea phalloides and Artemisia lerchiana.
ObjectLocationAOA
(mg GAE g−1 d.w.)
TP
(mg GAE g−1 d.w.)
Se
(µg kg−1 d.w.)
Proline
(mg g−1 d.w.)
Diploschistes ocellatusBaskunchak19.0 ± 1.6 b11.0 ± 1.0 b250 ± 20 d1.03 ± 0.10 c
Crimea *18.2 ± 1.6 b10.1 ± 1.0 b261 ± 21 d1.02 ± 0.10 c
Calvatia candidaBaskunchak21.1 ± 1.9 b12.1 ± 1.0 b590 ± 43 c1.31 ± 0.12 b
Crimea **21.4 ± 2.0 b11.7 ± 1.0 b850 ± 78 b1.22 ± 0.11 b
Battarrea phalloidesBaskunchak7.9 ± 0.7 c7.4 ± 0.7 c6140 ± 546 a1.12 ± 0.10 bc
Crimea **7.2 ± 0.7 c6.9 ± 0.6 c8130 ± 750 a1.09 ± 0.10 bc
Artemisia lerchianaBaskunchak68.6 ± 5.1 a21.0 ± 1.8 a135 ± 11 e5.45 ± 0.44 a
Crimea **58.5 ± 5.2 a24.1 ± 2.1 a116 ± 10.0 e5.29 ± 0.41 a
* Novy Svet, ** Karadag Nature Reserve. AOA—total antioxidant activity; TP—total polyphenols. Within each column, the values with the same letters do not differ statistically according to Duncan text at p < 0.05.
Table 4. Photosynthetic pigments content in Diploschistes ocellatus and Artemisia lerchiana.
Table 4. Photosynthetic pigments content in Diploschistes ocellatus and Artemisia lerchiana.
ParameterDiploschistes ocellatusArtemisia lerchiana
Chlorophyll a (mg 100 g−1 d.w.)6.18 ± 0.53 b41.70 ± 4.01 a
Chlorophyll b (mg 100 g−1 d.w.)13.80 ± 0.70 b91.00 ± 9.00 a
Total chlorophyll (mg 100 g−1 d.w.)19.98 ± 1.40 b132.70 ± 1.24 a
Chlorophyll b/Chlorophyll a ratio2.23 ± 0.20 a2.18 ± 0.20 a
Carotene (mg 100 g−1 d.w.)0.65 ± 0.05 b19.00 ± 1.6 a
Total chlorophyll/carotene ratio30.74 ± 3.00 a6.98 ± 0.70 b
Along each line, the values with the same letters do not differ statistically according to Duncan test at p < 0.05.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Golubkina, N.; Tolpysheva, T.; Lapchenko, V.; Lapchenko, H.; Pirogov, N.; Zaitsev, V.; Sękara, A.; Tallarita, A.; Stoleru, V.; Murariu, O.C.; et al. Comparative Evaluation of Antioxidant Status and Mineral Composition of Diploschistes ocellatus, Calvatia candida (rostk.) Hollós, Battarrea phalloides and Artemisia lerchiana in Conditions of High Soil Salinity. Plants 2023, 12, 2530. https://doi.org/10.3390/plants12132530

AMA Style

Golubkina N, Tolpysheva T, Lapchenko V, Lapchenko H, Pirogov N, Zaitsev V, Sękara A, Tallarita A, Stoleru V, Murariu OC, et al. Comparative Evaluation of Antioxidant Status and Mineral Composition of Diploschistes ocellatus, Calvatia candida (rostk.) Hollós, Battarrea phalloides and Artemisia lerchiana in Conditions of High Soil Salinity. Plants. 2023; 12(13):2530. https://doi.org/10.3390/plants12132530

Chicago/Turabian Style

Golubkina, Nadezhda, Tatiana Tolpysheva, Vladimir Lapchenko, Helene Lapchenko, Nikolay Pirogov, Viacheslav Zaitsev, Agnieszka Sękara, Alessio Tallarita, Vasile Stoleru, Otilia Cristina Murariu, and et al. 2023. "Comparative Evaluation of Antioxidant Status and Mineral Composition of Diploschistes ocellatus, Calvatia candida (rostk.) Hollós, Battarrea phalloides and Artemisia lerchiana in Conditions of High Soil Salinity" Plants 12, no. 13: 2530. https://doi.org/10.3390/plants12132530

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