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Article

Effect of Extracts from Dominant Forest Floor Species of Clear-Cuts on the Regeneration and Initial Growth of Pinus sylvestris L. with Respect to Climate Change

by
Vaida Sirgedaitė-Šėžienė
1,*,
Adas Marčiulynas
2 and
Virgilijus Baliuckas
3
1
Laboratory of Forest Plant Biotechnology, Institute of Forestry, Lithuanian Research Centre for Agriculture and Forestry, Liepų str. 1, LT-53101 Girionys, Kaunas District, Lithuania
2
Department of Forest Protection and Game Management, Institute of Forestry, Lithuanian Research Centre for Agriculture and Forestry, Liepų str. 1, LT-53101 Girionys, Kaunas District, Lithuania
3
Department of Forest Genetics and Tree Breeding, Institute of Forestry, Lithuanian Research Centre for Agriculture and Forestry, Liepų str. 1, LT-53101 Girionys, Kaunas District, Lithuania
*
Author to whom correspondence should be addressed.
Plants 2021, 10(5), 916; https://doi.org/10.3390/plants10050916
Submission received: 2 April 2021 / Revised: 26 April 2021 / Accepted: 29 April 2021 / Published: 2 May 2021
(This article belongs to the Special Issue Plant–Plant Allelopathic Interactions)
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Abstract

:
Climate change influences the ecological environment and affects the recruitment of plants, in addition to population dynamics, including Scots pine regeneration processes. Therefore, the impact of cover-dominant species extracts on the germination of pine seeds and morpho-physiological traits of seedling under different environmental conditions was evaluated. Increasing temperature reinforces the plant-donor allelochemical effect, reduces Scots pine seed germination, and inhibits seedling morpho-physiological parameters. Conditions unfavourable for the seed germination rate were observed in response to the effect of aqueous extracts of 2-year-old Vaccinium vitis-ideae and 1-year-old Calluna vulgaris under changing environmental conditions. The lowest radicle length and hypocotyl growth were observed in response to the effect of 1-year-old C. vulgaris and 2-year-old Rumex acetosella under increasing temperature (+4 °C) conditions. The chlorophyll a + b concentration in control seedlings strongly decreased from 0.76 to 0.66 mg g−1 (due to current environmental and changing environmental conditions). These factors may reduce the resistance of Scots pine to the effects of dominant species and affect the migration of Scots pine habitats to more favourable environmental conditions.

1. Introduction

Climate change, in combination with other factors, influences the ecological environment; subsequently, this clearly affects the recruitment and population dynamics of plants [1]. The early stages of the plant life-cycle are expected to be more sensitive to climate change than the adult stages and, as such, represent a major bottleneck for recruitment [2]. Seedling emergence is usually synchronized with seasonal changes in the environment [3]. Germination of some species occurs soon after dispersal, whereas that of other dormant species is postponed until a favourable season when the seedlings can survive, grow, and ultimately reproduce [4]. Due to the influence of post-germination traits and fitness, germination and possibly phenotypic plasticity on dormancy may be subject to strong selection [5]. Therefore, the pertinent issue is whether the adaptation of seeds and seedling traits can match the rate of climate change [6]. Moreover, such adaptation of annual (or herbaceous) species with rapid life cycles may occur more rapidly than that of perennial (or woody) species [7]. With respect to the plasticity and adaptations of tree species, very little is known about their germination behaviour in response to environmental changes [8,9].
The capacity of plants to adapt to changing climatic and environmental conditions is becoming a pressing issue, and has practical importance. Adaptation capacity differs for various plant species [10]. Climate change can challenge the adaptive capacity of many long-lived species, such as trees, and this adaptive capacity likely exceeds migration capacity [11,12]. Species with a wide distribution are especially useful for testing changes in recruitment patterns as a consequence of climate alterations because they grow under considerably different ecological conditions across their range. Scots pine (Pinus sylvestris L.) has the largest geographical distribution among pine species, and it is one of the most widespread conifers on Earth, distributed from the Mediterranean to the Arctic [13]. In the EU member states it constitutes approximately 20% of the commercial forest area and is of considerable importance as a timber-producing species, especially in the north of Europe [14].
Allelopathy, competition, soil nutrient imbalance, and poor ectomycorrhization have been implicated in conifer regeneration failure in the presence of dense ericaceous understory resulting from forest harvesting and fire in all ecosystem types. There are reports about allelochemical production in many woody species, such as in eucalyptus forests in Australia [15], in boreal conifer forests [16], tropical forests [17], temperate forests [18] and in subdesert communities [19]. Čaboun [20] noted that allelopathy is an important phenomenon for forest regeneration, population structure, and productivity. In forest ecosystems, allelopathy, which is one of the forms of plant competition, affects many plant characteristics, including abundance, growth, plant successions, plant population structure, dominance, diversity, and plant productivity [16]. It has an impact not only on natural regeneration, but also on reforestation, both for seeds germination and the initial growth of seedlings.
Within the forest floor litter, the dominant species of clear-cuts of Scots pine stands, which are mostly ericaceous, contain a range of secondary metabolites, mostly phenolic compounds, that are inhibitory to conifer seed germination, including primary root growth and ectomycorrhizal growth [16]. This inhibition can include planted tree seedlings that exhibit stunted growth in these forest areas with serious ecological, economic, and social consequences. Tree harvesting and inadequate management of the forest can cause long-term occupancy of a site by the understory and cover grown species with irreversible habitat degradation, which converts conifer forests into ericaceous heath [21]. The literature reports that allelopathic features of dominant species may depend on temperature and CO2 concentration changes, which are also associated with climate changes [22,23,24]. In addition, previous studies have shown that plant allelopathic properties and Scots pine responses to different temperature regimes vary considerably [25]. Mittler and Blumwald [26], and Ainsworth and Rogers [27] reported that Scots pine seedlings are more easily adaptable to changes in environmental conditions than to plant-dominant extracts. Other studies indicated pine seed germination and growth responses to elevated CO2 concentration [28]. The capacity of trees to capitalize on CO2 and convert it into carbohydrates results in better plant growth and yield [29]. This is called the CO2 fertilization effect and has received less attention compared with secondary climate change factors, such as increasing temperature [30]. Therefore, climate change scenarios have been modelled to predict the potential impact of dominant species of clear-cuts on natural forest regeneration and reforestation under changing climate conditions (temperature and carbon dioxide concentration).
Laboratory studies of allelopathic effect are affected by the knowledge gap associated with imitating natural conditions to evaluate the same processes of allelopathic phenomena. However, research on this topic is widely performed by creating different conditions and setting different goals to better understand certain aspects of this plant-plant interaction. It is important to recognize that it is sometimes impossible to mimic climate changes during laboratory experiments, as the studied plants are sensitive to indoor cultivation. According to our previous studies and literature analyses, the aqueous extracts of dominant forest-floor species have an allelopathic effect, which may have an impact on the morpho-physiological parameters of Scots pine initial growth. Therefore, this study aimed to evaluate the impacts of aqueous extracts produced from both shoots and roots of 1-year-old and 2-year-old dominant plants grown in clear-cuts of Scots pine (Vaccinio-Pinetum) stands in response to different temperature regimes and CO2 concentrations ex situ (in growing chambers). A complex experiment was designed to reveal the implications and interactions between allelopathic and plant developmental parameters (species and plant parts) in the germination of Scots pine seeds and morpho-physiological traits of seedlings.

2. Results

2.1. The Impact of Environmental Conditions on Seed Germination and Seedling Growth under the Effect of Plant Donors

Analysis of the impact of different environmental conditions (temperature and carbon dioxide) on Scots pine seed germination showed that the aqueous extracts of plant donors exhibited a higher allelopathic effect under increasing temperature (T—25.5/20 °C, CO2—400 ppm) and increasing temperature with higher CO2 concentrations (T—25.5/20 °C, CO2—700 ppm) (Figure 1).
RDA revealed that the rate of seed germination was the lowest as a response under conditions of increasing temperature with higher CO2 concentration (T—25.5/20 °C, CO20—700 ppm) (Figure 1). The rate of seed germination of Scots pine was more inhibited by 1-year-old clear-cuts of C. vulgaris shoot aqueous extracts than by those of other dominant species. In addition, the increasing temperature with higher CO2 concentration was more unfavourable for the rate of seed germination due to the effect of 2-year-old clear-cut shoot aqueous extracts of V. vitis-idaea (Figure 1).
A statistically significant decrease in the germination rate was determined in the effect of 2-year-old V. vitis-idaea (p < 0.05) and R. acetosella (p < 0.05), and 1-year-old C. vulgaris (p < 0.05) shoot extracts when the temperature increased from 21.5/16 °C to 25.5/20 °C and the CO2 concentration increased from 400 ppm to 700 ppm (Figure 2).
Statistical analysis (Table 1) revealed the statistically significant inhibition of C. vulgaris (p < 0.05) extracts and 2-year-old V. vitis-idaea (p < 0.05) shoot extracts on Scots pine seed germination rates when the temperature increased from 21.5/16 °C to 25.5/20 °C. The statistically significant lowest seed germination rate was recorded in the effect of the shoot extracts of C. epigejos (p < 0.05) under increasing temperature (25.5/20 °C) and higher (700 ppm) CO2 concentration conditions (Table 1).
Under conditions of increasing temperature and higher CO2 concentration, different plant donors and their parts exhibited a stronger inhibitory effect on the growth of Scots pine seedling radicles compared with the growth of Scots pine seedling hypocotyls (Figure 3).
According to RDA (Figure 3) analysis, the inhibitory effect on the growth of Scots pine radicles increased with increasing temperature (T—25.5/20 °C, CO2—400 ppm). The strongest inhibitory effect on the growth of Scots pine seedling radicles was determined in shoot aqueous extracts of 1-year-old V. vitis-idaea and P. schreberi, and of 2-year-old R. acetosella and C. epigejos. The results of our research (Figure 4) indicate that the radicle length was more inhibited in the effect of 1-year-old C. vulgaris (p < 0.05) and R. acetosella (p < 0.05) under increasing temperatures from 21.5/16 °C to 25.5/20 °C.
RDA revealed (Figure 5) that the increase in temperature from 21.5/16 °C to 25.5/20 °C significantly reduced the hypocotyl length due to the effect of the aqueous extracts of all plant-donors. In addition, under the increased temperature and higher CO2 concentration conditions (T—25.5/20 °C, CO2—700 ppm), plant-donor aqueous extracts exhibited lower inhibitory effects on the hypocotyl length of Scots pine (Figure 5).
The hypocotyl length of Scots pine seedling were more inhibited by the effect of shoot aqueous extracts of C. vulgaris of 1-year-old clear-cuts and R. acetosella of 2-year-old clear cuts than by those of other plant-donor species (Figure 6).
Statistical analysis revealed that the increase in temperature from 21.5/16 °C to 25.5/20 °C (Table 2) significantly reduced the radicle length due to the effect of shoot aqueous extracts of 2-year-old C. epigejos (p < 0.05) and R. acetosella (p < 0.05). The radicle length of Scots pine seedlings significantly decreased due to the effect of the shoot aqueous extracts of C. epigejos (p < 0.05), R. acetosella (p < 0.05), 1-year-old V. vitis-idaea (p < 0.05), and P. schreberi (p < 0.05) under conditions of increasing temperature with higher CO2 concentration conditions (T—25.5/20 °C, CO2—700 ppm) (Table 2).
The hypocotyl length of Scots pine seedlings significantly decreased due to the effect of shoot aqueous extracts of 2-year-old R. acetosella and 1-year-old C. vulgaris under conditions of an increase in temperature from 21.5/16 °C to 25.5/20 °C (p < 0.001 and p < 0.05, respectively), and an increase in temperature with higher (700 ppm) CO2 concentration (p < 0.01 and p < 0.05, respectively) (Table 2).

2.2. Allelopathic Effect on Photosynthetic Pigment Content under Different Environmental Conditions

The content of chlorophyll a + b of Scots pine seedlings was significantly affected by the shoot aqueous extracts of P. schreberi (p < 0.05), V. vitis-idaea (p < 0.05), and C. vulgaris (p < 0.01) under conditions of an increase in temperature from 21.5/16 °C to 25.5/20 °C (Figure 7). A lower inhibitory allelopathic effect on Scots pine seedling chlorophyll a + b content was determined for all plant-donor root aqueous extracts (Figure 7).
The allelopathic effect of plant-donor extracts under increasing temperature with higher CO2 concentration conditions was comparable to that obtained under increasing temperatures.
The Scots pine seedlings not affected by aqueous extracts of the plant-donor produced a higher content of carotenoids due to increasing temperature (Figure 8). Under conditions of increasing temperature with higher CO2 concentration, the higher CO2 concentration reduced the negative effect of the increasing temperature; therefore, the content of carotenoids was comparable to that obtained in the control, which amounted to 0.15 mg g−1 (Figure 8).
Plant-donor root aqueous extracts exhibited a lower negative impact on the carotenoid content of Scots pine seedlings (Figure 8). The highest changes in carotenoid content were determined in the effect of shoot aqueous extracts of V. vitis-idaea (p < 0.01) and root aqueous extracts of C. vulgaris (p < 0.01) under conditions of increasing temperature with higher CO2 concentration (T—25.5/20 °C, CO2—700 ppm). In addition, the increase in temperature significantly reduced the carotenoid content as a result of shoot aqueous extracts of 1-year-old P. schreberi (p < 0.01) and V. vitis-idaea (p < 0.01) and root aqueous extracts of 1-year-old C. vulgaris (p < 0.01) and 2-year-old C. epigejos (p < 0.01) (Figure 8).
The highest statistically significant inhibition of the chlorophyll a + b content in Scots pine seedlings was observed in the effect of shoot aqueous extracts of P. schreberi (p < 0.01) under conditions of increasing temperature from 21.5/16 °C to 25.5/20 °C with higher CO2 concentration (700 ppm) (Table 3).
Statistical analysis revealed the statistically significant inhibition of the chlorophyll a + b content of Scots pine seedlings due to the effect of root aqueous extracts of 1-year-old C. vulgaris (p < 0.01) and 2-year-old V. vitis-idaea (p < 0.01). The chlorophyll a + b content of Scots pine seedlings was more inhibited under conditions of increasing temperature with higher CO2 concentration (Table 3).
The strongest statistically significant inhibition of carotenoid concentration in Scots pine seedlings was recorded in the effect of shoot aqueous extracts of 1-year-old V. vitis-idaea (p < 0.001) and root aqueous extracts of 2-year-old C. epigejos (p < 0.001) in increasing temperature with higher CO2 concentration conditions (Table 3). Shoot aqueous extracts of 2-year-old C. epigejos (p < 0.01) and 1-year-old P. schreberi (p < 0.01) significantly changed the carotenoid concentration in Scots pine seedlings. This included root aqueous extracts of 1-year-old C. vulgaris (p < 0.01) and 2-year-old V. vitis-idaea (p < 0.01) under conditions of increasing temperature with higher CO2 concentration (T—25.5/20 °C, CO2—700 ppm) (Table 3).

2.3. Interaction between Plant-Donor Species and Environmental Conditions

Variance analysis showed (Table 4) that not only climate conditions but also the interaction between the dominant species and environmental conditions had a significant impact on the germination rate and the carotenoid content.
The radicle length (p < 0.01) and hypocotyls (p < 0.05) were mostly affected by the interaction between the dominant species and environmental conditions in addition to the pH of the species extracts. The environmental conditions and the dominant species were the primary indicators that most significantly contributed to variability in the obtained estimates. In addition, it was determined that the pH of the species extracts significantly affected the germination rate (p < 0.01) and the carotenoid content (p < 0.05). A statistically significant low-positive correlation (r = 0.21) was determined between the extract pH and the germination rate. A low positive correlation (r = 0.25) was found between the extract pH and the carotenoid content.

3. Discussion

Our findings show that the higher temperature was the main factor that increased the inhibitory effect of plant-donor aqueous extracts on germination of seeds and initial growth of seedlings. However, a study conducted by Ruan et al. [3] observed that the rising environmental temperature could increase the inhibitory effect of the aqueous extracts of P. schrenkiana needles on the seed germination and seedling growth of P. schrenkiana. At the germination stage, the influence of the roots of dominant plants is more important, because the seed is affected by processes occurring in the soil. Allelochemical produced by a donor plant determines its mobility in water, volatility in air, affinity to soil surfaces, and degradability [31].
According to our results, the increasing CO2 concentration recused the initial growth of Scots pine seedlings. In addition, the most favourable conditions for the length of hypocotyls were observed at current environmental conditions. Studies conducted by some authors indicated pine seed germination and growth responses to elevated CO2 concentration [28]. They indicated contradictory results that the seedings of Pinus pinea L. and that Pinus sylvestris L. were more sensitive to higher CO2 concentrations. Other authors [26,27] reported that Scots pine seedlings are more adaptable to changes in environmental conditions than to plant-dominant extracts. Many C3 plant species, particularly trees and C3 grasses, can capitalize on CO2 and convert it into carbohydrates due to increases in the photosynthesis rate, which results in better growth and yield [29]. Because of this generally positive assessment, which is sometimes called the CO2 fertilization effect, CO2 itself seems to receive less attention compared with secondary climate-change factors, such as increasing temperature [30]. The positive effects of CO2 could be welcomed, or even necessary to offset the anticipated negative impacts of high-temperature stress [22]. Mahmoodzadeh et al. [30] noted that, under unfavourable environmental conditions, different plant donors and their parts exhibited a stronger inhibitory effect on the seedling radicle compared to that on hypocotyl growth in Scots pine stands. Our results indicated that seed germination exhibited a different response to the root and shoot extracts of dominant species under different environmental conditions. Moreover, some authors have indicated that allelochemical production could be genetically regulated [31,32,33], and that allelochemical concentration depends on plant age [34,35]. Our results confirm these findings and indicate significant differences in Scots pine morpho-physiological parameters due to the effect of extracts of V. vitis-idaea of different ages.
The failure of natural regeneration and growth inhibition of planted conifers, such as black spruce, in the presence of Kalmia angustifolia L., and Ledum groenlandicum L. has been reported by several authors [36,37]. The ericaceous shrubs in coastal oceanic temperate rainforests and several Vaccinium species (e.g., Vaccinium alaskaense L.) in high elevation forests have been reported to cause growth stagnation of conifers such as Tsuga plicata Donn, Thuja heterophylla (Raf. Sarge), Picea sitchensis, and Abies amabilis Dougl. [38,39,40]. In sub-alpine spruce forests Vaccinium myrtillus L. has been reported to cause the regeneration failure of Picea abies (L) Karst. [41]. Phenolic allelochemicals of forest floor humus and seed predation have been implicated in this regeneration failure [42,43]. Experiments have been designed to determine the interactions between tree seedlings and ericaceous plants manifested via direct contact of dominant plant roots and tree seedling roots [44,45].
The inhibitory effect of different plant-donor part extracts on photosynthetic pigment under different environmental conditions might be due to the imbalance in metabolism regulated by various enzyme activities [46]. The structure of the plasma membrane may become denatured by the allelochemicals present in the shoot extract. The effect of different donor-plant parts has also been indicated in studies by other authors [30,47,48]. The photosynthetic pigments content was mostly affected by increasing CO2 concentrations [28]. This process might be related to a decrease in chlorophyll a/b-binding proteins, which could reduce the risk of photooxidative damage due to the relative decrease in the absorption cross-section of photosystems [48]. Alexieva et al. [29] noted out that the increase in the content of photosynthetic pigments depended on plant adaptation to changing conditions, that is, a defensive reaction to a stress agent (for example, increasing temperature and CO2 concentration). Existing local adaptations that allow individuals to tolerate environmental conditions are especially important to increase the resistance and resilience of current populations. As mentioned previously, the chlorophyll content and the radicle length may be used as key parameters in studies because of their sensitivity to allelopathic compounds [49]. Plant allelochemicals adversely affect chlorophyll biosynthesis and accumulation by interfering in chlorophyll biosynthesis and/or destruction. The subsequent negative effects of these processes inhibit photosynthesis and plant growth [50].
Any alterations in the plant community structure that are caused by climate change result from underlying changes in the population dynamics of the species that make up the community [51]. In an environmental context, it is very difficult to predict the results of climate change on allelopathic processes, but additional synergic or antagonistic interactions between allelochemicals and environmental conditions could be expected during experiments [52]. Therefore, understanding the responses to climate change at the species level is important to predict the functioning of the ecosystem in the future [53]. Species with higher adaptive capacity may remain, but the risk of a loss of genetic diversity could increase. Furthermore, the competitiveness of various plant species may be affected by the changing climate.

4. Materials and Methods

4.1. Dominant Species

The study of the successional stages of herbaceous plant and shrub phytocoenoses was conducted in one-year-old and two-year-old clear-cuts after reforestation of Pinetum vacciniosum forests in June-July of 2015. In total, seventeen clear-cuts were evaluated, including eight one-year-old and nine two-year-old clear cuts in the Trakai Forest Enterprise in the south-eastern part of Lithuania (54°30′–54°38′ N, 24°50′–25°00′ E). Aiming to determine the dominant species, the frequency (%) and relative plant cover (%) of ground vegetation species were estimated in 1 m2 subplots (n = 25) along transect in every 5 m in each site. The assessment was undertaken using the Braun–Blanquet [54] scale. The soil in the site was classified as Arenosol [55]. The forest type of the site was Pinetum vacciniosum, and the forest site type was Nb (oligotrophic mineral soil of normal moisture), according to the Lithuanian classification [56]. The mean annual temperature in Lithuania is 6.5 °C, and the mean annual precipitation is 686 mm.
During the assessment of dominant species of the experimental plots in the one-year-old clear-cut after reforestation, the highest frequency was found to be of Pleurozium schreberi and Vaccinium vitis-idaea (97% and 95%, respectively). Calluna vulgaris was the third most dominant species in the 1-year-old clear-cut at a frequency of 87%. The relative plant cover of Vaccinium vitis-idaea increased by 2%,reached 12%, and maintained its dominant position in relation to other plants in the two-year-old clear-cuts. The highest frequencies in the 2-year-old clear-cut after reforestation were recorded for Calamagrotis epigejos and Rumex acetosella, of 44% and 68% respectively. These two species were classified as dominant due to their vigorous and various spreading abilities (both generative and vegetative), and these species structurally altered the phytocoenosis that was previously established in the clear-cuts.
Subsequently, the dominant species (plant-donors) were used for production of aqueous extracts for the assessment of their allelochemical impact on potential acceptor species. Seed germination and seedling growth of the acceptor plant (Pinus sylvestris L.) were assessed as the main indicators of the morphophysiological traits of dominants on the initial stages of forest regeneration in the clear-cuts.

4.2. Laboratory Bioassays

The fresh dominant plants were sampled in the 1-year-old and 2-year-old forest clear-cuts after reforestation at mid-day. Each sample was collected in three replicates of dominant plants from three 1-year-old and three 2-year-old forest clear-cuts. The samples were transported to a laboratory in plastic bags. For the production of 0.2% aqueous extract concentrations, air-dried plant parts (roots and shoots) were chopped into 2 cm sized pieces. Twenty grams of biomass were placed in glass bottles filled with 100 mL of distilled water; then, the samples were covered with foil, shaken several times, maintained for approximately 12 h at 18 to 20 °C, and filtered. This procedure was in a previous study [25].
For the assessment, 100 sterilized Scots pine seeds were obtained from the Forest Seed and Plant Quality Department of the Lithuanian State Forest Service. It should be noted that Scots pine plus trees in Lithuania were selected mainly from the Pinetum vacciniosum forest type and soil conditions are similar to the current experiment’s soils. The composition of genotypes in seed orchards is broad in origin, so genetic diversity is also expected to be large. Pine seeds for the experiment were taken from the seed lots of several previous years and a mixture of seed orchards. The applicability of the results is defined by the forest type and soil conditions that actually prevail in pine stands in Lithuania. Pine stands occupy the largest forest area in Lithuania. Scots pine seeds were placed on filter paper in a Petri dish with a 9-cm-diameter. Five milliliters of 0.2% extract were added to each Petri dish and covered. For the control, 100 seeds were sown in distilled water. An additional 5 milliliters of distilled water and aqueous extracts from the dominant plants were added to Petri dishes every five days during the germination period. Each variant was performed in triplicate. The total number of Petri dishes was 324 (2 ages of clear-cuts × 3 replicates of clear-cuts × 3 dominant species × 2 plant parts × 3 different experimental conditions × 3 replicates × 3 replicates of Petri dishes = 324 Petri dishes).
To evaluate the impact of different temperatures and CO2 concentrations on the allelopathic activity of dominant plants, the influence of different dominant species and plant parts on the germination and seedling growth of the Scots pine was assessed. The laboratory trials were carried out in the laboratory of Vytautas Magnus University. For the seed germination process, all Petri dishes were stored in chambers with controlled temperatures and CO2 conditions that consisted of three different temperatures and CO2 concentrations for 21 days. The photoperiod was 14 h, the air humidity was 75%, and the photosynthetic photon flux density was approximately 200 μmol m2 s−1 in all chambers. Light was provided by the combination of six natural fluorescent lamps (Philips, Waterproof OPK Natural Daylight LF80 Wattage 2 W/TL-D 58 W) and one high-pressure sodium lamp (Philips MASTER GreenPower CG T 600 W). The Petri dishes were exposed to the following temperatures and CO2 concentrations:
  • the first three chambers (current environmental conditions)—temperature of 21.5/16 °C at day/night with 400 ppm CO2,
  • the second three chambers (increasing temperature (+4 °C) conditions)—25.5/20 °C with 400 ppm CO2,
  • the third three chambers (increasing temperature with higher CO2 concentration conditions)—25.5/20 °C with 700 ppm CO2.
The photoperiod, air humidity, and photosynthetic photon flux density were automatically adjusted. The temperatures and CO2 concentrations were controlled by the PC-based Environmental Control System (computer software IGSS 9-13175).
Measurements of Scots pine seedlings were performed. The germinated seeds were counted (in units) at day 21. Germination rates (G,%) were calculated relative to germination in the control (C) according to the formula [57]:
G = (Gv × 100)/C
Gv—is the number of germinated seeds per unit in the experiment, C - is the number of germinated seeds in the control equated to 100%.
At day 21 the radicle and hypocotyl lengths (mm) were measured and deducted as a percentage of control as germination rate.
In addition, 0.2 g of fresh pine seedling shoots was sampled for chlorophyll a and b (chl a and b) and carotenoid assays. For the determination of pigment content, the method of Wettstein [58] was used, as described in a previous study [59]. The content of carotenoids and chl a and b (mg g-1) was estimated spectrophotometrically using the T80 UV-VIS spectrophotometer (PG Instruments, Leicestershire, UK) at wavelengths of 441, 662 and 644 nm (D), respectively. For the calculation of pigment content, the following formulas were used:
chl a = 9.784 × D 662 − 0.990 × D 664 c × V P × 1000 ,
chl b = 21.426 × D 644 − 4.650 × D 662 c × V P × 1000 ,
Carotenoid = 4.695 × D 440.5 − 0.268 × ( chl a + b ) c × V P × 1000 ,
where c is the pigment content (mg g−1), V is the extract volume (mL), and P is the fresh mass of seedling needles (g).
Laboratory analyses were performed at the Institute of Forestry of the Lithuanian Research Centre for Agriculture and Forestry (LAMMC).

4.3. Statistical Data Analysis

The significance of the data was assessed based on Wilkin’s λ-test and Fisher’s theoretical criterion (F). The results of the allelopathic effects were statistically evaluated using the statistical package STATISTICA from Stat Soft. SAS UNIVARIATE procedure was used to check if residuals followed normal distribution. Based on the results on residual distribution, the Student t-test (t) or Kolmogorov–Smirnov (KS) test was used in pairwise comparison to determine statistically significant differences (* p < 0.05, ** p < 0.01, *** p < 0.001) in germination rates and morphophysiological parameters under different temperature regimes (analysed using the XLSTAT software). The Kruskal–Wallis test was used for a group of treatments. Redundancy analysis (RDA) was used to determine relationships between different environmental conditions and the effects of dominant species and their parts on Scots pine germination rate and morphometric parameters (analysed using XLSTAT software). The SAS MIXED procedure (REML method) was used to obtain variance components of random effects and significances of fixed effects. The effects of fixed parameters, that is, temperature and the extract pH group (if 2.0 < pH ≤ 4.9, then the pH group = 1; if 4.9 < pH ≤ 5.9, then the pH group = 2; and if 5.9 < pH < 7.0, then pH group = 3) were evaluated using the TEST3 method.
The initial SAS MIXED procedure was performed according to the following model.
y i j k l m n = μ + s i + p j + h k + r l + d m + r h l k + d h m k + r s l i + d s m i + ε i j k l m n ,
where yijklmn is the response value for the n-th observation, µ is the overall mean, si is the fixed effect for the i-th temperature, pj is the fixed effect for the j-th replication, hk is the fixed effect for the k-th pH group, rl is the random effect for the l-th species, dm is the random effect for the m-th plant part, rhlk is the random effect for the interaction of the l-th species and the k-th pH group, dhmk is the random effect for the m-th plant part and k-pH group interaction, rsli is the random effect for the l-th species and i-th temperature interaction, dsmi is the random effect for the m-th plant part, the i-th temperature interaction, and εijklmn is the random error.Furthermore, the study included a series of models with fixed effects from model (4) but with a single random effect. Therefore, we arrived at six models associated with respective random effects. This part of the statistical analysis was performed using the SAS software (SAS 9.4) [60].

5. Conclusions

The assessment of climate conditions revealed the inhibitive properties of dominant extracts on seed germination under changing environmental conditions ex situ (a temperature of 25.5 °C during the day and 20 °C at night and 700 ppm of CO2). However, the morphometric parameters of the seedlings remained unchanged. Higher air temperature resulted in a stronger negative effect, which decreased pine germination and seedling growth. The CO2 concentration of 700 ppm induced better growth of pine seedlings but decreased the concentration of photosynthetic pigments. The main effect on the germination of Scots pine seeds and morpho-physiological parameters of seedlings was induced by different environmental conditions and interactions between plant-donor species and climatic conditions.
It can be assumed that the new findings obtained regarding the changes in the allelopathic potential of dominant species in the clear-cuts of previous Scots pine stands in Lithuania will improve the understanding of the impact of allelopathy on reforestation and the further management of forest ecosystems under changing climate conditions.

Author Contributions

Conceptualization, V.S.-Š. and A.M.; methodology, V.S.-Š.; software, V.B.; investigation, V.S.-Š.; data curation, V.B.; writing—original draft preparation, V.S.-Š. and V.B.; writing—review and editing, V.S.-Š., A.M. and V.B.; visualization, V.S.-Š. and V.B. All authors have read and agreed to the published version of the manuscript.

Funding

This research is funded by the European Social Fund under the No 09.3.3-LMT-K-712 “Development of Competences of Scientists, other Researchers and Students through Practical Research Activities” measure.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Dalgleish, H.J.; Koons, D.N.; Adler, P.B. Can life history traits predict the response of forb populations to changes in climate variability? J. Ecol. 2010, 98, 209–217. [Google Scholar] [CrossRef]
  2. Donohue, K.R.; De Casas, R.; Burghardt, L.; Kovach, K.; Willis, C. Germination, postgermination adaptation, and species ecological ranges. Annu. Rev. Ecol. Evol. Syst. 2010, 41, 293–319. [Google Scholar] [CrossRef]
  3. Ruan, X.; Pan, C.D.; Liu, R.; Li, Z.H.; LI, S.L.; Jiang, D.A.; Zhang, J.C.; Wang, G.; Zhao, Y.X.; Wang, Q. Effects of climate warming on plant autotoxicity in forest evolution: A case simulation analysis for Picea schrenkiana regeneration. Ecol. Evol. 2016, 6, 5854–5866. [Google Scholar] [CrossRef]
  4. Walck, J.L.; Hidayati, S.N.; Dixon, K.W.; Thompson, K.; Poschlod, P. Climate change and plant regeneration from seed. Glob. Chang. Biol. 2011, 17, 2145–2161. [Google Scholar] [CrossRef]
  5. Evans, A.S.; Cabin, R.J. Can Dormancy Affect the Evolution of Post-Germination Traits? The Case of Lesquerella Fendleri. Ecology 1995, 76, 344–356. [Google Scholar] [CrossRef]
  6. Hovenden, M.J.; Wills, K.E.; Chaplin, R.E.; Vander Schoor, J.K.; Williams, A.L.; Osanai, Y.U.I.; Newton, P.C. Warming and elevated CO2 affect the relationship between seed mass, germinability, and seedling growth in Austrodanthonia caespitosa, a dominant Australian grass. Glob. Chang. Biol. 2008, 14, 1633–1641. [Google Scholar] [CrossRef]
  7. Ibanez, I.; Clark, J.S.; LaDeau, S.; Hille Ris Lambers, J. Exploiting temporal variability to understand tree recruitment response to climate change. Ecol. Monogr. 2007, 77, 163–177. [Google Scholar] [CrossRef]
  8. Hedhly, A.; Hormaza, J.I.; Herrero, M. Global warming and sexual plant reproduction. Trends Plant Sci. 2009, 14, 30–36. [Google Scholar] [CrossRef] [PubMed]
  9. Logant, B.; Pieters, A.B.; Andrewg, B.; Scott, J.G. Plant response to climate change along the forest-tundra ecotone in northeastern Siberia. Glob. Chang. Biol. 2013, 19, 3449–3462. [Google Scholar]
  10. Parmesan, C.; Hanley, M.E. Plants and climate change: Complexities and surprises. Ann. Bot. 2015, 116, 849–864. [Google Scholar] [CrossRef] [PubMed]
  11. Rehfeldt, G.E.; Tchebakova, N.M.; Parfenova, Y.I.; Wykoff, W.R.; Kuzmina, N.A.; Milyutin, L.I. Intraspecific responses to climate in Pinus sylvestris. Glob. Chang. Biol. 2002, 8, 912–929. [Google Scholar] [CrossRef] [Green Version]
  12. Jump, A.S.; Mátyás, C.; Peńuelas, J. The altitude-for-latitude disparity in the range retractions of woody species. Trends Ecol. Evol. 2009, 24, 694–701. [Google Scholar] [CrossRef] [Green Version]
  13. Matias, L.; Jump, A.S. Interactions between growth, demography and biotic interactions in determining species range limits in a warming world: The case of Pinus sylvestris. For. Ecol. Manag. 2014, 282, 10–22. [Google Scholar] [CrossRef]
  14. Mason, W.L.; Alia, R. Current and future status of Scots pine (Pinus sylvestris L.) (Eds). Silviculture and Biodiversity of Scots pine Forests in Europe. For. Syst. 2000, 1-2000, 317–333. [Google Scholar]
  15. Lovett, J.H. Allelopathy: The Australian experience. In The Science of Allelopathy; Putnam, A.R., Tang, C.-S., Eds.; John Wiley & Sons: New York, NY, USA, 1986; pp. 75–99. [Google Scholar]
  16. Mallik, A.U. Conifer regeneration problems in boreal and temperate forest with ericaceous understory: Role of disturbance, seedbed limitation, and keystone change. Crit. Rev. Plant Sci. 2003, 22, 341–366. [Google Scholar] [CrossRef]
  17. McKey, D.; Waterman, P.G.; Mbi, C.N.; Gartlon, J.S.; Strubraker, T.T. Phenolic content of vegetation in two African rain forests: Ecological implications. Science 1978, 202, 61–63. [Google Scholar]
  18. Willianson, G.B.; Richardson, D.R.; Fischer, N.H. Allelopathic mechanism in fire-prone communities. In Allelopathy: Basic and Applied Aspects; Rizvi, S.J.H., Rizvi, V., Eds.; Chapman & Hall: London, UK, 1992; pp. 57–75. [Google Scholar]
  19. Van Rooyen, M.W.; Theron, G.K.; van Rooyen, N.; Jankowitz, W.J.; Matthews, W.S. Mysterious circles in the Namib Desert: Review of hypotheses on their origin. J. Arid. Env. 2004, 57, 467–485. [Google Scholar] [CrossRef]
  20. Čaboun, V. Results of allelopathy research in Slovak forest ecosystems. In Proceedings of the Second European Allelopathy Symposium “Allelopathy—From understanding to application”, Pulawy, Poland, 3–5 June 2004; p. 24. [Google Scholar]
  21. Reigosa, M.J.; Pedrol, N.; Gonzalez, L. Allelopathy: A Physiological Process with Ecological Implications; Springer: Dordrecht, The Netherlands, 2006. [Google Scholar]
  22. Tausz, M.; Tausz-Posch, S.; Norton, R.M.; Fitzgerald, G.J.; Nicolas, M.E.; Seneweera, S. Understanding crop physiology to select breeding targets and improve crop management under increasing atmospheric CO2 concentrations. Environ. Exper. Bot. 2013, 88, 71–80. [Google Scholar] [CrossRef]
  23. Goufo, P.; Pereira, J.; Moutinho-Pereira, J.; Correia, C.M.; Figueiredo, N.; Carranca, C.; Rosa, E.A.S.; Trindade, H. Rice (Oryza sativa L.) phenolic compounds under elevated carbon dioxide (CO2) concentration. Environ. Exper. Bot. 2014, 99, 28–37. [Google Scholar] [CrossRef]
  24. Zhang, Q.; Zhang, Y.; Peng, S.; Zobel, K. Climate Warming May Facilitate Invasion of the Exotic Shrub Lantana camara. PLoS ONE 2014, 9, e105500. [Google Scholar] [CrossRef] [Green Version]
  25. Sirgedaitė-Šėžienė, V.; Baležentienė, L.; Varnagirytė-Kabašinskienė, I.; Stakėnas, V.; Baliuckas, V. Allelopathic effects of dominant ground vegetation species on initial growth of Pinus sylvestris L. seedlings in response to different temperature scenarios. iForest Biogeosci. For. 2019, 12, 132–140. [Google Scholar] [CrossRef]
  26. Mittler, R.; Blumwald, E. Genetic engineering for modern agriculture: Challenges and perspectives. Annu. Rev. Plant Biol. 2010, 61, 1–20. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  27. Ainsworth, E.A.; Rogers, A. The response of photosynthesis and stomatal conductance to rising [CO2]: Mechanisms and environmental interactions. Plant Cell Environ. 2007, 30, 258–270. [Google Scholar] [CrossRef] [PubMed]
  28. Lütz, C.; Anegg, S.; Gerant, D.; Alaoui-Sosse, B.; Gerard, J.; Dizengremel, P. Beech treles exposed to high CO2 and to simulated summer ozone levels: Effects on photosyntesis, chloroplast components and leaf enzime activity. Physiol. Plant. 2000, 109, 252–259. [Google Scholar] [CrossRef]
  29. Alexieva, V.; Ivanov, S.; Sergiev, I.; Karanov, E. Interaction between stresses. Bulg. J. Plant Physiol. 2003, 29, 1–17. [Google Scholar]
  30. Mahmoodzadeh, H.; Ghasemi, M.; Zanganeh, H. Allelopathic effect of medicinal plant Cannabis sativa L. on Lactuca sativa L. seed germination. Acta Agric. Slov. 2015, 105, 233–239. [Google Scholar] [CrossRef]
  31. Blanco, J.A. The representation of allelopathy in ecosystem level forest models. Ecol. Model. 2007, 209, 65–77. [Google Scholar] [CrossRef]
  32. Quader, M.; Daggard, G.; Barrow, R.; Walker, S.; Sutherland, M.W. Allelopathy, DIMBOA production and genetic variability in accessions of Triticum speltoides. J. Chem. Ecol. 2001, 27, 747–760. [Google Scholar] [CrossRef]
  33. Marčiulynas, A.; Sirgedaitė-Šėžienė, V.; Žemaitis, P.; Baliuckas, V. The Resistance of Scots Pine (Pinus sylvestris L.) Half-sib Families to Heterobasidion annosum. Forests 2019, 10, 287. [Google Scholar] [CrossRef] [Green Version]
  34. Wolfson, J.L.; Murdock, L.L. Growth of Manduca sexta on wounded tomato plants: Role of induced proteinase inhibitors. Entomol. Exp. Appl. 1990, 54, 257–264. [Google Scholar] [CrossRef]
  35. Šėžienė, V.; Baležentienė, L.; Maruška, A. Identification and Biological Activity of Phenolic Compounds in Dominant’ Extracts of Pine Forest Clear-Cuts. iForestry 2017, 10, 309–314. [Google Scholar] [CrossRef] [Green Version]
  36. Yamasaki, S.H.; Fyles, J.W.; Egger, N.E.; Titus, B.D. The effect of Kalmia angustifolia on growth, nutrition, and ectomycorrhizal symbiont community of black spruce. For. Ecol. Manag. 1998, 105, 197–207. [Google Scholar] [CrossRef]
  37. Mallik, A.U. Growth and physiological responses of black spruce (Picea mariana) to sites dominated by Ledum groenlandicum. J. Chem. Ecol. 1996, 22, 575–585. [Google Scholar]
  38. Messier, C. Factors limiting early growth of western red cedar, western hemlock and Sitka spruce seedlings on ericaceous–dominated clearcut sites in coastal British Columbia. For. Ecol. Manag. 1993, 60, 181–206. [Google Scholar] [CrossRef]
  39. Prescott, C.E.; Weetman, G.F. Salal Cedar Hemlock Integrated Research Program: Research Update # 1; Faculty of Forestry, University of British Columbia: Vancouver, BC, Canada, 1996; p. 49. [Google Scholar]
  40. Fraser, L.; Chanway, C.P.; Turkington, R. The competitive role of Gaultheria shallon on planted western hemlock and western red cedar saplings on northern Vancouver Island. For. Ecol. Manag. 1995, 75, 27–39. [Google Scholar] [CrossRef]
  41. Jaderlund, A.; Zackrisson, O.; Nilsson, M.-C. Effects of bilberry (Vaccinium myrtillus L.) litter on seed germination and early seedling growth of four boreal tree species. J. Chem. Ecol. 1996, 22, 973–986. [Google Scholar] [CrossRef]
  42. Gallet, C.; Lebreton, P. Evolution of phenolic patterns and associated litter and humus of a mountain forest ecosystem. Soil Biol. Biochem. 1995, 27, 157–165. [Google Scholar] [CrossRef]
  43. Gallet, C.; Nilsson, M.-C.; Zackrisson, O. Phenolic metabolites of allelopathic significance in Empetrun hermaphroditum leaves and associated humus. Plant Soil 1999, 210, 1–9. [Google Scholar] [CrossRef]
  44. Nilsson, M.-C. Separation of allelopathy and resource competition by the boreal dwarf shrub Empetrum hermaphroditum Hagerup. Oecologia 1997, 98, 1–7. [Google Scholar] [CrossRef]
  45. Jäderlund, A.; Zackrisson, O.; Dahlberg, A.; Nilsson, M.C. Interference of Vaccinium myrtillus on establishment, growth, and nutrition of Picea abies seedlings in a northern boreal site. Can. J. For. Res. 1997, 27, 2017–2025. [Google Scholar] [CrossRef]
  46. Becklin, K.M.; Anderson, J.T.; Gerhart, L.M.; Wadgymar, S.M.; Wessinger, C.A.; Ward, J.K. Examining Plant Physiological Responses to Climate Change through an Evolutionary Lens. Plant Physiol. 2016, 172, 635–649. [Google Scholar] [CrossRef] [PubMed]
  47. Gulzar, A.; Siddiqui, M.B. Allelopathic effect of aqueous extracts of different part of Eclipta alba (L.) Hassk. on some crop and weed plants. J. Agric. Ext. Rural Dev. 2014, 6, 55–60. [Google Scholar]
  48. Heidarzadeh, A.; Pirdashti, H.; Esmaeili, M.A.; Asghari, J. Inhibitory Activity of Allelochemicals on Barnyardgrass (Echinochloa crus-galli L.) Seed and Seedlings Parameters. World Appl. Sci. J. 2012, 17, 1535–1540. [Google Scholar]
  49. Rashedmohasel, M.J.; Mousvi, S.K. Principles of Weed Management; Ferdowsi University of Mashhad Publication: Mashhad, Iran, 2007; pp. 273–290. [Google Scholar]
  50. Wang, R.L.; Zeng, R.S.; Peng, S.L.; Chen, B.M.; Liang, X.T.; Xin, X.W. Elevated temperature may accelerate invasive expansion of the liana plant Ipomoea cairica. Weed Res. 2011, 51, 574–580. [Google Scholar] [CrossRef]
  51. Bellard, C.; Bertelsmeier, C.; Leadley, P.; Thuiller, W.; Courchamp, F. Impacts of climate change on the future of biodiversity. Ecol. Lett. 2012, 15, 365–377. [Google Scholar] [CrossRef] [Green Version]
  52. Gomes, M.P.; Garcia, Q.S.; Barreto, L.C.; Pimenta, L.P.S.P.; Matheus, M.T. Allelopathy: An overview from micro- to macroscopic organisms, from cells to environments, and the perspectives in a climate-changing world. Biologia 2017, 72, 113–129. [Google Scholar] [CrossRef]
  53. Balčiūnas, M.; Jankauskienė, Z.; Brazaitytė, A.; Duchovskis, P. The effect of plant stand density on plant leaf area index and content of photosynthetic. Zemdirb. Agric. 2008, 95, 97–109. [Google Scholar]
  54. Braun-Blanquet, J. Pflanzensoziologie: Grundzüge der Vegetationskunde, 3rd ed.; Springer Wien: New York, NY, USA, 1964; p. 865. [Google Scholar]
  55. WRB. World Reference Base for Soil Resources; International Soil Classification System for Naming Soils and Creating Legends for Soil Maps; World Soil Resources Reports No. 106; FAO: Rome, Italy, 2014; p. 191. [Google Scholar]
  56. Vaičys, M.; Beniušis, R.; Karazija, S.; Kuliešis, A.; Raguoti, A.; Rutkauskas, A. Classification of forest sites. Forest Site Types; LUTUTĖ: Kaunas, Lithuania, 2006; p. 95. [Google Scholar]
  57. ISTA. Method Validation for Seed Testing; The International Seed Testing Association (ISTA): Basedorf, Switzerland, 2007; p. 66. [Google Scholar]
  58. Wettstein, D. Chlorophyll Letale und der submikroskopishe Formveschsel der Plastiden. Exp. Cell Res. 1957, 12, 427. [Google Scholar] [CrossRef]
  59. Sirgedaitė-Šėžienė, V.; Mildažienė, V.; Žemaitis, P.; Ivankov, A.; Koga, K.; Shiratani, M.; Baliuckas, V. Long-term response of Norway spruce to seed treatment with cold plasma: Dependence of the effects on the genotype. Plasma Process. Polym. 2021, 18, 2000159. [Google Scholar] [CrossRef]
  60. SAS Institute Inc. SAS/STAT® User’s Guide; Version 9.3; SAS Institute Incorporated: Cary, NC, USA, 2010. [Google Scholar]
Plants 10 00916 g001 550
Figure 1. RDA of the impact of the shoots (black triangles) and roots (black squares) of plant-donor aqueous extracts on germination at different climate conditions (1—Current environmental conditions (21.5/16 °C and 400 ppm CO2 concentration), 2—temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), 3—Increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (*): dominant species of 2-year-old clear-cuts.
Figure 1. RDA of the impact of the shoots (black triangles) and roots (black squares) of plant-donor aqueous extracts on germination at different climate conditions (1—Current environmental conditions (21.5/16 °C and 400 ppm CO2 concentration), 2—temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), 3—Increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (*): dominant species of 2-year-old clear-cuts.
Plants 10 00916 g001
Plants 10 00916 g002 550
Figure 2. The impact of climate conditions on Scots pine seed germination rate under the effect of plant-donor shoot (a) and root (b) extracts (mean±SD, *—p < 0.05 post-hoc LSD test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20°C and 700 ppm CO2). (2) - dominant species of 2-year-old clear-cuts.
Figure 2. The impact of climate conditions on Scots pine seed germination rate under the effect of plant-donor shoot (a) and root (b) extracts (mean±SD, *—p < 0.05 post-hoc LSD test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20°C and 700 ppm CO2). (2) - dominant species of 2-year-old clear-cuts.
Plants 10 00916 g002
Plants 10 00916 g003 550
Figure 3. RDA of the impact of the shoots (black triangles) and roots (black squares) of plant-donor aqueous extracts on radicle length at different climate conditions (1—Current environmental conditions (21.5/16 °C and 400 ppm CO2 concentration), 2—temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), 3—increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (*): dominant species of 2-year-old clear-cuts.
Figure 3. RDA of the impact of the shoots (black triangles) and roots (black squares) of plant-donor aqueous extracts on radicle length at different climate conditions (1—Current environmental conditions (21.5/16 °C and 400 ppm CO2 concentration), 2—temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), 3—increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (*): dominant species of 2-year-old clear-cuts.
Plants 10 00916 g003
Plants 10 00916 g004 550
Figure 4. The impact of climate conditions on Scots pine radicle length under the effect of plant-donor shoot (a) and root (b) extracts (mean±SD, *—p < 0.05 Kruskal–Wallis test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (2)—dominant species of 2-year-old clear-cuts.
Figure 4. The impact of climate conditions on Scots pine radicle length under the effect of plant-donor shoot (a) and root (b) extracts (mean±SD, *—p < 0.05 Kruskal–Wallis test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (2)—dominant species of 2-year-old clear-cuts.
Plants 10 00916 g004
Plants 10 00916 g005 550
Figure 5. RDA of the impact of the shoots (black triangles) and roots (black squares) of plant-donor aqueous extracts on hypocotyl length at different climate conditions (1—Current environmental conditions (21.5/16 °C and 400 ppm CO2 concentration), 2—temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), 3—increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (*): dominant species of 2-year-old clear-cuts.
Figure 5. RDA of the impact of the shoots (black triangles) and roots (black squares) of plant-donor aqueous extracts on hypocotyl length at different climate conditions (1—Current environmental conditions (21.5/16 °C and 400 ppm CO2 concentration), 2—temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), 3—increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (*): dominant species of 2-year-old clear-cuts.
Plants 10 00916 g005
Plants 10 00916 g006 550
Figure 6. The impact of climate conditions on Scots pine hypocotyls length under the effect of plant-donor shoot (a) and root (b) extracts (mean ± SD, *—p < 0.05 Kruskal–Wallis test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (2)—dominant species of 2-year-old clear-cuts.
Figure 6. The impact of climate conditions on Scots pine hypocotyls length under the effect of plant-donor shoot (a) and root (b) extracts (mean ± SD, *—p < 0.05 Kruskal–Wallis test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (2)—dominant species of 2-year-old clear-cuts.
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Plants 10 00916 g007 550
Figure 7. Chlorophyll concentration in the Scots pine seedlings under the effect of plant-donor shoot (a) and root (b) extracts under different CO2 and temperature conditions (*—p < 0.05 post-hoc LSD test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (2)—dominant species of 2-year-old clear-cuts.
Figure 7. Chlorophyll concentration in the Scots pine seedlings under the effect of plant-donor shoot (a) and root (b) extracts under different CO2 and temperature conditions (*—p < 0.05 post-hoc LSD test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (2)—dominant species of 2-year-old clear-cuts.
Plants 10 00916 g007
Plants 10 00916 g008 550
Figure 8. Carotenoid concentration in the Scots pine seedlings under the effect of plant-donor shoot (a) and root (b) extracts under different CO2 and temperature conditions (*—p < 0.05 post-hoc LSD test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (2)—dominant species of 2-year-old clear-cuts.
Figure 8. Carotenoid concentration in the Scots pine seedlings under the effect of plant-donor shoot (a) and root (b) extracts under different CO2 and temperature conditions (*—p < 0.05 post-hoc LSD test). Control conditions (21.5/16 °C and 400 ppm CO2 concentration), temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2). (2)—dominant species of 2-year-old clear-cuts.
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Table
Table 1. Overall difference between treatment groups and between the treatments (n = 9) for germination rate under different climate conditions (* p < 0.05, ** p < 0.01, *** p < 0.001).
Table 1. Overall difference between treatment groups and between the treatments (n = 9) for germination rate under different climate conditions (* p < 0.05, ** p < 0.01, *** p < 0.001).
Age of Clear-CutsExtractPlant-DonorPr > Chi-SquareClimate Conditions
1/3 11/23/2
1-year-oldShootP. schreberi0.2380
V. vitis-idaea0.0156
C. vulgaris0.0066***
RootV. vitis-idaea0.0581
C. vulgaris0.1275
2-year-oldShootV. vitis-idaea0.0007****
C. epigejos0.0012* *
R. acetosella0.0144*
RootV. vitis-idaea0.0002**
C. epigejos0.0668
R. acetosella0.0147**
1 1—Current environmental conditions (21.5/16 °C and 400 ppm CO2 concentration), 2—Temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), 3—Increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2).
Table
Table 2. Overall difference between treatment groups and between the treatments (n = 9) for radicle and hypocotyl length (mm) responses to extracts under different climate conditions (* p < 0.05, ** p < 0.01, *** p < 0.001).
Table 2. Overall difference between treatment groups and between the treatments (n = 9) for radicle and hypocotyl length (mm) responses to extracts under different climate conditions (* p < 0.05, ** p < 0.01, *** p < 0.001).
Age of Clear-CutsExtractPlant-DonorPr > Chi-SquareComparison of Treatments
1/3 11/23/21/31/23/2
Radicle lengthHypocotyl lengthRadicle lengthHypocotyl length
1-year-oldShootP. schreberi0.04770.8503 *
V. vitis-idaea0.84410.4291 *
C. vulgaris0.93330.0903
RootV. vitis-idaea0.86300.8708
C. vulgaris0.81790.6439
2-year-oldShootV. vitis-idaea0.25280.9828
C. epigejos0.15890.6139
R. acetosella0.04970.0012 ** *****
RootV. vitis-idaea0.95210.8082
C. epigejos0.86550.8391
R. acetosella0.95540.9176
1 1—Current environmental conditions (21.5/16 °C and 400 ppm CO2 concentration), 2—Temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), 3—Increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2).
Table
Table 3. Overall difference between treatment groups and between the treatments (n = 9) for chlorophyll (mg g−1) and carotenoid (mg g−1) concentrations under different climate conditions (* p < 0.05, ** p < 0.01, *** p < 0.001).
Table 3. Overall difference between treatment groups and between the treatments (n = 9) for chlorophyll (mg g−1) and carotenoid (mg g−1) concentrations under different climate conditions (* p < 0.05, ** p < 0.01, *** p < 0.001).
Age of Clear-CutsExtractPlant-DonorPr > Chi-SquareComparison of Treatments
1/3 11/23/21/3 11/23/2
Chlorophyll a + bCarotenoidChlorophyll a + bCarotenoid
1-year-oldShootP. schreberi0.00080.0008 **** ****
V. vitis-idaea0.0042<.0001** *****
C. vulgaris0.76020.0150 *
RootV. vitis-idaea0.09500.0638
C. vulgaris0.0003<.0001**** *******
2-year-oldShootV. vitis-idaea0.72410.0414 *
C. epigejos0.05990.0003 ****
R. acetosella0.83450.6707
RootV. vitis-idaea0.00950.0010 ** ****
C. epigejos0.20130.0495
R. acetosella0.08370.0108 *
1 1—Current environmental conditions (21.5/16 °C and 400 ppm CO2 concentration), 2—Temperature increases of 4 °C compared to the current conditions (25.5/20 °C and 400 ppm CO2 concentration), 3—Increasing temperature with higher CO2 concentration conditions (25.5/20 °C and 700 ppm CO2).
Table
Table 4. Variance components and standard errors of random effects as well as the F criterion and significance (p-value) of fixed effects from separate analyses for each trait (* p < 0.05, ** p < 0.01, *** p < 0.001).
Table 4. Variance components and standard errors of random effects as well as the F criterion and significance (p-value) of fixed effects from separate analyses for each trait (* p < 0.05, ** p < 0.01, *** p < 0.001).
ParameterVariance Component of Interaction between Dominant Species and Climate Conditions (%±SE)Pr > ZClimate ConditionspH
F criterionp-valueF criterionp-value
Germination17.42±9.57*7.41**7.01***
Radicle length38.67±17.06**0.33-13.03***
Hypocotyl length22.49±11.14*0.87-8.08***
Carotenoid9.17±5.16*12.23***3.89*
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Sirgedaitė-Šėžienė, V.; Marčiulynas, A.; Baliuckas, V. Effect of Extracts from Dominant Forest Floor Species of Clear-Cuts on the Regeneration and Initial Growth of Pinus sylvestris L. with Respect to Climate Change. Plants 2021, 10, 916. https://doi.org/10.3390/plants10050916

AMA Style

Sirgedaitė-Šėžienė V, Marčiulynas A, Baliuckas V. Effect of Extracts from Dominant Forest Floor Species of Clear-Cuts on the Regeneration and Initial Growth of Pinus sylvestris L. with Respect to Climate Change. Plants. 2021; 10(5):916. https://doi.org/10.3390/plants10050916

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Sirgedaitė-Šėžienė, Vaida, Adas Marčiulynas, and Virgilijus Baliuckas. 2021. "Effect of Extracts from Dominant Forest Floor Species of Clear-Cuts on the Regeneration and Initial Growth of Pinus sylvestris L. with Respect to Climate Change" Plants 10, no. 5: 916. https://doi.org/10.3390/plants10050916

APA Style

Sirgedaitė-Šėžienė, V., Marčiulynas, A., & Baliuckas, V. (2021). Effect of Extracts from Dominant Forest Floor Species of Clear-Cuts on the Regeneration and Initial Growth of Pinus sylvestris L. with Respect to Climate Change. Plants, 10(5), 916. https://doi.org/10.3390/plants10050916

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