Valasia Iakovoglou · Ioannis Takos ·Georgia Pantazi · Aikaterini Pipsou ·Maria Neofotistou

Abstract Restoration activities in semi-arid Mediterranean areas like Greece face many obstacles, such as summer droughts that are becoming more intense with climate change, that pose limitations to transplanting success. Seedlings for restoration must be of high quality; a vigorous root system is critical to enable seedlings to tolerate adverse conditions. Here we investigated the effects of altitude and source parent for seeds on the growth of subsequent seedlings to determine the best seed sources for obtaining highest-quality, most-tolerant seedlings for restoration efforts.Seeds of Quercus coccifera L. were collected on an altitudinal gradient of 50 m (200, 250 and 300 m a.s.l.) and from specif ic parents at each altitude. Subsequent seedlings were grown for 3 months in a greenhouse with controlled irrigation. The results indicated a strong altitudinal and parental seed effect on seedling characteristics. As altitude decreased,biomass of the seedlings increased, and they developed more vigorous roots and more photosynthetic leaf tissue. Thus,altitude and parent are critical factors to consider when producing seed-derived seedling. By collecting seeds from a specif ic altitude and parent, more vigorous and stresstolerant seedlings can be obtained to enhance transplanting success.

Keywords Climate c hange · Conservation · Nursery practices · Regeneration · Seedling p hysiology

Introduction

Reforestation efforts in semi-arid Mediterranean areas such as Greece are usually associated with high mortality levels,mainly due to intense and frequent drought events, especially during the summer. Such drought events have been predicted to increase in severity and duration at an alarming level (Xoplaki et al. 2005; Lionello et al. 2006; IPCC 2013).Climate change is thus expected not only to pose obstacles to reforestation efforts (Villar-Salvador et al. 1999; Rude 2007) and the growth of the species (Olivar et al. 2015),but also to threaten the species existence when they cannot adapt quickly to abrupt climatic alterations (Gritti et al.2006; Allen et al. 2010; Thomas and Garcia-Marti 2015).The ecological responses of a species to adapt and perpetuate is associated with a shift in its distributional range toward higher latitudes and altitudes (Korpel et al. 1982; Penuelas and Boada 2003; Saha et al. 2016).

Specif ic characteristics such as vigorous roots enable seedlings to overcome transplanting stress that is usually associated with water def icit, a common problem in Mediterranean ecosystems (Bellot et al. 2002; David et al. 2016).Extensive root systems favor faster absorption and enhanced exploration into a wider area and greater soil depth for water and nutrients (Ackerly 2004; Villar-Salvador et al. 2005;Lambers et al. 2006; Mitchell et al. 2008). Factors such as the parental seed source and seed size can also inf luence the attributes of the generated seedlings; larger seeds produce more vigorous seedlings (Iakovoglou et al. 2007; Iakovoglou et al. 2008). In addition, as altitude increases, trees become more stunted, and seed production and germination percentage decrease (Mencuccini et al. 1995; Robakowski et al. 1997; Loha et al. 2006; Coomes and Allen 2007).Research has also indicated that in terms of seedling growth and biomass allocation, seed sources from lower altitudes resulted to more vigorous seedlings (Dierig et al. 2006; Iakovoglou et al. 2017), while in other cases the results were contradictory (Liu et al. 2016). Nonetheless, to our knowledge,limited research has been conducted in addressing the effect of altitudinal seed sampling gradient on the characteristic of the produced seedlings for Mediterranean broadleaved species.

Here we investigated the growth traits ofQuercus cocciferaL. (kermes oak; Fagaceae) seedlings in relation to the altitude and parent origin of the seed. We hypothesized that both altitude and parent would affect growth of the seedlings, with an increase in altitude associated with reduced seedling growth. By studying the impact of seeds gathered on an altitude gradient on subsequent seedling growth, we can gain insights that will guide nurseries when collecting seeds at a specif ic altitude to generate seedlings with growth traits such as vigorous root systems that will favor tolerance to adverse conditions and thus increase transplanting success in reforestation efforts.

Material a nd methods

Seed c ollection

Quercus cocciferawas selected because it is an evergreen,sclerophyllous, broadleaved species that thrives in Mediterranean semi-arid ecosystems (Ca?ellas and San Miguel 2000). It is usually found in a shrubby form, mainly due to intense grazing activities. It can tolerate intensely adverse growth conditions and maintain its vigor under poor and dry soils (Papatheodorou et al. 1998; Konstantinidis et al.2005). This is mainly due to its ability to grow vigorous root systems that enable the species to better exploit water and nutrient resources (Benayas et al. 2007; Verdaguer et al.2011). Consequently, it is ecologically very valuable, since it provides food and shelter to the wildlife and livestock in areas where other species fail (Benayas et al. 2007), while its vigorous roots and thick foliage prevent soil erosion (Ca?ellas and San Miguel 2000).

Before seed collection, at least 60 open-crown (crown growth not limited by competitive plants), healthyQ. cocciferashrubs (20 at each altitude) were closely monitored and marked to guarantee an adequate number of seeds for the experiment. Seeds were collected on an altitudinal gradient of 50 m (200, 250 and 300 m a.s.l.) and only from a westfacing aspect (24°09′, 41°08′) in northern Greece to minimize climatic variation, particularly from rainfall events, that substantially affect the size and number of seeds produced and plant growth. The main collection criterion was seed color; brown is a good indicator of proper seed maturity(Bonner and Vozzo 1987).

After seed collection (20 trees per altitude), healthyappearing seeds were placed in water for a 24-h imbibition;damaged and insect-infested seeds were discarded (Bonner and Vozzo 1987; Gribko and Jones 1995). For each parent at each altitude, the seeds were separated based on their widest diameter by using digital calipers and were placed in polyethylene bags (Gosling 1989), then cold-stratif ied at 4± 1 °C for 4 months to break seed dormancy. Only pre-germinated seeds with a maximum diameter of 12-4 mm were sown to minimize any seed-size effect on seedling growth(Iakovoglou et al. 2007; Iakovoglou et al. 2008). Of the 20 closely monitored shrubs, four parents per altitude provided adequate pre-germinated seeds to complete the experiment.The seeds were sown in containers (1.5 L) of a 3:1 peat to perlite mixture. The seedlings were grown for 3 months in a greenhouse (～25 °C) with consistent daily irrigation and no fertilization.

Studied v ariables

At the end of 3 months, eight seedlings from each parent at each altitude (96 total seedlings) were harvested. After careful removal of the soil substrate, the seedlings were separated into their subparts and evaluated. Leaf area (LA)was measured by using a leaf area meter (AM 100, ADC Bioscientif ic, Herts, UK). Dry mass (g) of the seedlings and their subparts (leaves [LDW], stem (STDW] and roots[RDW]). Total dry mass of the shoot (SDW) was determined as LDW + STDW, and total seedling dry mass (TSDW)was estimated by the partitioning of LDW+STDW+RDW(Iakovoglou et al. 2008). The ratio of root to shoot dry mass(RDW/SDW) was estimated and specif ic leaf area (SLA)was calculated as the ratio of the leaf area to leaf dry mass(LA/LDW). The percentage of biomass allocation to the leaves (LDW/TSDW), stems (STDW/TSDW) and roots(RDW/TSDW) was also calculated.

Statistical anal yses

One-way ANOVA was used to compare means of various traits of seedlings among the three altitudes with the program SPSS v. 15.0 (SPSS, Chicago, IL, USA). Data were tested for normality and homogeneity. The general linear model was used to determine the effect of altitude, parent and their interaction. Mean differences were tested with the Tukey’s multiple range tests at signif icance levels ofp＜0.01 (**) andp＜ 0.05 (*). Pearson’s correlation analysis was performed to determine the signif icance of the relationship among the studied variables

W),mass (RD DW W/TS 1*30**- 0.8 W) and roots 0.20), root drySD RD- 0.529**- 0.526**- 0.566**0.216*- 0.570**- 0.248*0.979**36**- 0.6/T DW W SD DW/T ass (ST DW 6**), stem (ST- 0.254*0.59 2**0.26 ST- 0.581**W), stemW d/rTyS mDW DW W/TS*.217*.227 1**0**6**.824*4***mass (LD g of leaves (LD LD*- 0- 0 0.597**0.62 0.30 0.54 0.29- 0- 0.255*), leaf dry A 8*3**SL 0.25 0.24- 0.379**- 0.259*- 0.381**- 0.409**0.249*40**- 0.360**leaf area (LA- 0.5 A) and biomass partitionin- 0.5 Ratio 57**55**- 0.5 88**-- 00..5288**) and their interactionon DW 87**ot ratio (Ratio), specifi c leaf area (SL 25***TS****- 0.2- 0.3 0.822*0.912**0.793**0.873**0.923**1 level*****0.0 W.262.337 9**e (A), parent seed (PS SD***- 0- 0 0.909**0.975**0.886**0.61 55*- 0.2 W 37****-sho RD****- 0.2 0.527*0.629*0.497*f altitud), root-to*0**.250 DW nifi cant correlation at *0.05 and *ig M analysis showing signifi cant eaffs se c(Tt SoDW ST**- 0. S 0.76 etween the studied variables 0.01 1**0.732**W) at p ＜W), total seedling dry m ld seedlings LD*****- 0.307**- 0.352**0.92 and (**onth-o 30*97**0.05-m****- 0.2- 0.2)LA ass (SD earson’s correlation analysis b GL)W) for 3-Table 1ry m Ratio AW/TS/T shoot d/TSD M analysis Altitude (A)SDDW Altitude (A)PS Pearson’s correla analysis i cant (*) effect at p ＜Parent seed (PS DW if DW W(REff ect GL Parent seed (PS A ×tion LA LDW DWW W DW ST RD SD TS SL LDDW W/TS ST RD Results of the P Sign

Fig. 1 The effect of altitude (m a.s.l.) on growth traits of 3-monthold seedlings. The studied growth traits were the leaf area (LA), dry mass of leaves (LDW), stems (STDW), roots (RDW), shoots (SDW),total dry mass of seedlings (TSDW), root to shoot ratio (Ratio) and specif ic leaf area (SLA). Different letters indicate signif icant differences among altitudes for each variable at p ＜ 0.05

Results

There was a strong effect of both the altitude and parent on the majority of the studied variables. Specif ically, the altitudinal gradient affected LA, LDW, RDW, SDW, TSDW, SLA and LDW/TSDW (Table 1 A). Similarly, a parental effect was evident for the LA, LDW, STDW, RDW, SDW and TSDW,with an interaction effect for the LA and LDW. Based on the Pearson’s correlation analysis results, both the altitude and parent tree were negatively correlated with LA, LDW, RDW,SDW, TSDW and LDW/TSDW, with the parent also being negatively correlated with the STDW (Table 1 B).

Seedlings derived from seeds from lower altitudes had greater mean values for all growth traits (LA, LDW, RDW,SDW and TSDW) except SLA compared with those from seedlings from seeds from higher altitudes (Fig. 1).

The effect of altitude was also supported by the results of the percentage allocations of biomass (Fig. 2). Seedlings derived from seed sources of lower altitudes (200 m a.s.l.)had greater LDW than those of the higher altitudes (250 and 300 m a.s.l.), whereas altitude did not signif icantly affect the percentage of allocation to stems or roots.

Discussion

Altitude and parent seed source had a strong effect on the growth ofQ. cocciferaseedlings (Table 1 A); the altitudinal effect was greater, with seedlings from seeds at lower altitudes outperforming those from higher altitude sources(Fig. 1). Thus, even just a 50-m difference in altitude affected growth traits of the seedlings. These results coincide with results for seedlings ofQ. cocciferafrom seeds along an altitudinal gradient of 100 m (Iakovoglou et al. 2017) and forPinus f lexilis(Reinhardt et al. 2011). Pearson’s correlation analysis also supported these results with a negative correlation among altitude and all but one trait (LA, LDW, RDW,SDW, TSDW and the LDW/TSDW); SLA was positively correlated (Table 1 B). These results show that altitude is a strong factor that should always be considered when collecting seeds for seedling production, since specif ic characteristics such as more vigorous root systems are associated with lower altitude seed sources.

Particularly forQ. coccifera, which is characterized by its vigorous root systems (Benayas et al. 2007; Verdaguer et al.2011), seedlings from seeds from lower altitudes allocated more of the total biomass to the root systems. Seedlings with vigorous root systems can take up more water and nutrients, which coincides with potentially greater reforestation success (Bellot et al. 2002). So, particularly for semi-arid Mediterranean areas such as Greece, those seedlings with better root systems are better equipped to grow in stressful conditions, particularly droughts, when regenerating a site,and transplanting success should potentially increase.

Further, the greater leaf area and leaf dry mass forQ.cocciferaof seedlings from the lower altitudinal sources indicates that those seedlings are better equipped for light harvesting. Nonetheless, those seedlings were also characterized by lower SLA values, indicating that they had thicker leaves, which enables the species to adapt and tolerate adverse growth conditions (Coomes and Allen 2007).Because leaf characteristics for species such asQ. cocciferaare related to the overall seedling performance, leaf measurements such as LA and SLA, could be used as a less-labor intensive measure to estimate seedling growth than rootrelated traits. Those results were also supported by Pearson’s correlation analysis, which showed that the leaf characteristics LA and LDW were positively correlated with the majority of the other seedling characteristics (STDW, RDW, SDW,TSDW and LDW/TSDW), but negatively correlated to the Ratio and the RDW/TSDW (Table 1 B).

The effect of altitude on the characteristics of the produced seedlings was also evident by the percentage of biomass allocation (Fig. 2). So, leaf biomass allocation differed among altitudes, with greater mean value for the lower altitude of 200 m a.s.l. This result shows that, even forQ. cocciferain which vigorous roots play a dominant role in shaping the physiological ability of the species to thrive under harsh environments, leaves also play a crucial role in survival.

Similar to the altitudinal effect, a parental effect was evident for the majority of the studied variables (LA, LDW,STDW, RDW, SDW and TSDW) (Table 1 A), coincident with results forQuercus macrocarpaandQ. alba(Iakovoglou et al. 2007, 2008). Although we minimized the impact of climatic and edaphic variations on the seeds by selecting parents that were growing near each other on the same westfacing aspect, the parental effect was still evident. These results were also supported by the Pearson’s correlation analysis where “parent” was correlated with nine of the 11 studied variables (Table 1 B). These correlations with the parent might indicate that pre-selected genetic attributes enable the survival and competitiveness of those parents at a specif ic altitude (Tang and Ide 2001; Nakagawa 2003).Those attributes were passed to the produced seeds, enabling seedling growth with specif ic characteristics (such as more vigorous root systems) that made them more competitive than other seedlings. Consequently, careful selection of vigorous parent trees is critical to generate vigorous seedlings that have larger root systems and more leaf area.

Fig. 2 Percentage of biomass allocation for seedlings derived from seeds at three altitudes (200, 250 and 300 m a.s.l.). Different letters indicate signif icant differences among altitudes for each variable at p＜ 0.05

Based on the results of our study, collecting seeds from lower altitudes is recommended for obtaining more vigorous seedlings, especially to increase transplanting success when regenerating areas with adverse conditions such as severe droughts. Hence, this research provides foundation for future research on growing seedlings to restore higher altitude sites and determining whether the genetic characteristics of a less-f it high-altitude seedlings are worth conserving. Further research should include a wider variety of species and stresses (e.g., water def icit) to increase transplanting success and productivity of certain forest species when challenged by climatic change.

Conclusion

In this study of the effect of altitudinal seed source and parent on growth traits of the resultant seedlings, an altitudinal gradient of 50 m was sufficient to inf luence growth of the seedlings, even though climatic and edaphic variation was minimized by sampling specif ic-sized seed from a westfacing aspect. Seeds from lower altitudes produced more vigorous seedlings, with greater root systems for enhanced water absorption and more leaf area for greater photosynthetic capacity, as opposed to higher altitudes. Further, leaf characteristics (e.g., SLA) indicated that those seedlings could better cope and tolerate abrupt climatic alterations,particularly droughts. Thus, forQ. coccifera, seeds should be harvested from lower altitudes to provide more vigorous seedlings that are better equipped (vigorous roots and thicker leaves) to tolerate water def icits and thus increase regeneration success. Future research on more and diverse species should help expand our knowledge on the altitudinal effects on parent seeds and subsequent seedling growth.

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