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The Climatic Response of Tree Ring Width Components of Ash (Fraxinus excelsior L.) and Common Oak (Quercus robur L.) from Eastern Europe

This paper aims to develop the first differentiated (earlywood—EW, latewood—LW, and total ring width—RW) dendrochronological series for ash (Fraxinus excelsior L.) and oak (Quercus robur L.) trees from the Republic of Moldova, and to analyze their climatic response and their spatio-temporal stability. For this, 18 ash and 26 oak trees were cored from the Dobrus, a protected area, Republic of Moldova, Eastern Europe, and new EW, LW, and RW chronologies were developed for ash and oak covering the last century. The obtained results showed that the RW and LW have a similar climatic response for both species, while EW is capturing interannual climate variations and has a different reaction. The analyses performed with monthly climatic data revealed a significant and negative correlation with the mean air temperature and a significant and positive correlation with precipitation and the Standardized Precipitation-Evapotranspiration Index (SPEI) for both ash and oak. The temperature during the vegetation period has a strong influence on all tree-ring components of ash, while for oak the strong correlation was found only for LW. The positive and significant correlation between LW and RW with precipitation for both species, suggests that ash and oak are sensitive to the hydrological component and the precipitation is the main tree growth-limiting factor. Despite the significant correlation with precipitation and temperature for the whole analyzed period, the 25-year moving correlation analyses show that they are not stable in time and can switch from positive to negative or vice versa, while the correlation with SPEI3 drought index, which is a integration of both climatic parameters, is stable in time. By employing the stability map analysis, we show that oak and ash tree ring components, from the eastern part of the Republic of Moldova, have a stable and significant correlation with SPEI3 and scPDSI drought indices from February (January) until September, over the eastern part of Europe.


Introduction
Climate models predict an increase of mean surface temperature over large regions of Europe, including the Republic of Moldova (Eastern Europe) [1]. As a consequence, the intensity, frequency, and duration of extreme events, especially heatwaves and drought, will increase and can lead to forest ecosystems stability degradation, which can contribute to increased risk of desertification. This process has already been observed in Central-Eastern Europe [2] and has serious consequences for forest ecosystems, in terms of ecological stability and productivity [3]. Forest susceptibility to climate change has increased and the adaptive capacity has dropped mainly due to increasing frequency and intensity of drought events [4,5]. Future climate changes have the potential to induce shifts in species composition and distribution, highly affecting biodiversity and specific ecological amplitude and overall forest services [3,[5][6][7][8][9].
In the Republic of Moldova, oak species (Quercus sp.) are the most spread species reaching 44.1% from the total forest area, while ash (Fraxinus sp.) represents only 5.7%, and it is found mostly in oak mixed forests [10]. Both species are vulnerable to climate changes and reports of forest growth decline and mortality linked to climate change have been recorded and studied throughout Europe [4,6,8,9,[11][12][13][14], as well as in North America [15][16][17] and Japan [18] being a worldwide phenomenon.
Oaks are widely studied in most of the dendro-related domains (dendrochronology, dendroclimatology, dendroarcheology, dendroecology, etc.) due to its longevity, spreading, climate sensitivity, timber use, and being widely chosen as construction wood since the dawn of harvesting tools development. In Europe, there are several studies regarding the oak reaction to climate, highlighting specific dendroclimatic patterns [3,14,[19][20][21][22][23][24][25][26][27]. The main outcomes from all these studies show that ash and oak are highly sensitive to precipitation and this is the main limiting growth factor. In general, oak tree rings chronologies correlate positively with precipitation from spring to summer, while the summer temperature response is unstable from site to site and the correlation can be found as either negative or positive.
In the 21st century, an increase of studies regarding ash forest decline and/or death phenomena has been reported, all induced by climate forcing, fungi (Hymenoscyphus fraxineus), or insect outbreaks [28][29][30][31]. Even if ash is widely spread, there are only a few dendrochronological studies in Europe, and the in-depth information on its response to climate and behavior is scarce and most studies have a dendroecological approach [32][33][34]. Several authors managed to compare oak and ash, using tree rings widths as a response to environmental conditions, in floodplains and river terraces [26,[35][36][37], and all pointed to the fact that ash is more sensitive to environmental changes. In this context, it is necessary to enhance our knowledge related to those species' responses in distinctive climate conditions. These climate-induced changes have to be faced and counterbalanced with adaptive silvicultural measures derived from a scientific-based management strategy [4,38,39]. Thus, to develop scientific-based decision support tools, it is necessary to gather new information regarding how main forest tree species respond to climate variability. This new information needs to be focused on both the response patterns, as well as its temporal stability.
The Republic of Moldova represents an unstudied area in dendrochronological studies, and this contribution intends to complete the overall image of oak and ash behavior by adding the required information for this specific area, characterized by excessive climate influences, with severe and frequent drought events [40]. As a consequence, it is necessary to fill in this knowledge gap and provide valuable information that can be used for future management strategies. As such, the main objectives of this study are (i) to develop the first differentiated (earlywood, latewood, and total ring width) dendrochronological series for ash and oak from the Republic of Moldova, Eastern Europe; (ii) to test the climate response of ash and oak; (iii) to analyze of the spatio-temporal stability of the climate-growth relationship.

Site Description
Ash (Fraxinus excelsior) and oak (Quercus robur) are among the most distributed tree species in Europe covering large areas with contrasting environmental conditions ( Figure 1A) [41]. As we move forward in the Eastern European plain, many tree species have to face more excessive continental influences, thus growing conditions being suboptimal [42]. The sampling site is located in the Dobrus , a protected area, part of Nistru Plateau, the Eastern part of the Republic of Moldova ( Figure 1A). The study site is located at an altitude of 250 m a.s.l. with a mean slope of 12 • (Figure 1A,B). The bedrock is represented by Sarmatian deposits covered with a layer of soft loam and phaeozem soil. The vegetation type is a mixed forest of oak, ash, and other broadleaf species (hornbeam, lime tree, Norway maple) [43]. The climate is characterized by a temperate continental climate (dry and hot summers and harsh winters) [40] (Figure 1A-C). The multiannual mean temperature is +8.7 • C and the annual precipitation amount is 445 mm, with high variability during the year. From the total precipitation amount, around 380 mm (85%) are recorded from April to October (≈196 days) and only 15% throughout the rest of the year (November to March). The Walter-Lieth climatic diagram shows a dry period at the end of the vegetation season (July and August) ( Figure 1C).

Chronology Development
In 2019, we selected 18 ash and 26 oak dominant healthy trees. Each tree was cored with Pressler borer at breast high (1.30 m), one core per tree. The increment cores were processed and measured in Forest Biometrics Laboratory, "Stefan cel Mare" University of Suceava (https:// erris.gov.ro/ Forest-Biometrics-Laboratory). Surface preparation of increment cores was made by cutting plane surfaces using the WSL core microtome [44]. The increment cores were scanned using Silverfast v.8.1 software and an EPSON 11000 XL flatbed scanner with 1600 dpi true resolution and saved in a 48bit color image format. CooRecorder v.9.31 software [45] was used to measure tree ring-widths (RW) as well as earlywood (EW) and latewood widths (LW) from the imagines, according to IAWA classification [46]. All measurements were individually cross-dated using TSAPwin [47] and statistically verified with COFECHA [48] using correlation analysis of 50-year intervals with 25-year overlaps [48,49]. To evaluate the agreement between different tree ring components and between species, standard dendrochronological statistics like Gleichläufigkeit-glk [50] and modified t value (tVBP) [51] were applied.
To remove the biological and potential non-climatically induced low-to medium-term growth trends, each individual raw data series was transformed into a growth index series. All tree ring components series (EW, LW, and RW) were detrended using an age dependent-spline [52] in ARSTAN v.48 software [53]. The initial spline stiffness related to tree age was set at 20 yrs., after that, the spline rigidity increases year by year. The mean chronologies (standard chronology) for each species and tree ring components were obtained using a bi-weight mean [54,55]. The strength of the chronological signal was evaluated with the expressed population signal (EPS) parameter, using a 30-yrs. window length with 15-yrs. overlap [56]. The EPS threshold value was set to 0.85, as it is widely accepted [57]. Additionally, the standard dendrochronological statistics (e.g., mean sensitivity (MS), first-order autocorrelation (AC1), inter-series correlation (rbar), variability explained by first principal component (%var) and signal to noise ratio (SNR)) were computed.
The climate growth relationship was performed based on monthly climatic variables and each differentiated chronology for both species. The correlations coefficients were computed for a time interval between June, the previous year, until September, the current year. The statistical significance of the correlations was evaluated by bootstrap methods (p = 0.05) using R environment [61] with the treeclim package [62]. Additionally, the Pearson correlation coefficients were calculated for SPEI values over the cumulative time-scale spectrum (from 1 to 24 months) and presented as correlation heat maps in ggplot2 library [63].
To test the dendroclimatic temporal stability, we computed the moving correlations for seasonal periods, from the previous autumn (August to November, ason), the current spring (March to May, MAM) and the current summer (June to August, JJA) for both mean temperature and precipitation. The moving correlation was also performed for the August SPEI index, for 3, 6, 12, and 18 months of cumulative periods. The analysis was made using a 25-years moving window with a one-year step.

Stability Maps
To examine the stationarity of the long-term relationship between the tree-ring based proxies and the gridded climate parameters (e.g., maximum, mean and minimum temperature, precipitation, drought indices-SPEI3 and scPDSI) we made use of stability maps, a method successfully used in the seasonal forecast of European rivers and Arctic sea ice [64,65]. To detect stable relationships, the variability of the correlation between the tree ring proxies and the climate parameters was investigated within a 31-year moving window within the analyzed period. The correlation was considered stable for those regions where the tree rings proxies and climate parameters were significantly correlated at the 90% or 80% level for more than 80% of the moving window. A detailed description of the methodology is given in [66]. This methodology has been successfully used for the first time in dendroclimatological studies by [67]. The advantage of this methodology, when compared with traditional correlation analysis, is that is able to identify just the regions which have a stable relationship in time with our tree rings-based proxies.

Chronologies Characteristics
In this study, we developed the first EW, LW, and RW oak chronologies for the Republic of Moldova, and one of the first EW-LW chronologies for ash in Europe ( Figure 2D). The maximum period covers the 1871-2018 period for ash and the 1853-2018 period for oak. The mean tree age is 130 years for ash and 109 years for oak. In terms of growth performance, oak RW is higher (2.98 ± 1.61mm) compared to ash (2.01 ± 0.98mm), these differences being preserved for all tree ring components (Table 1). Table 1. Statistical parameters for ash (Fraxinus excelsior) and oak (Quercus robur) chronologies (AGR-annual growth rate; MS-mean sensitivity; AC1-first-order autocorrelation; rbar-inter-series correlation; EPS-expressed population signal; %var-explained variance; SNR-signal-to-noise-ratio).

Species
Ring The EW proportion from RW is almost similar for oak (36%) and ash (38%). The 20 yrs. low pass filters have shown similar growth trends for both LW and RW chronologies without obvious differences between the two species, while EW recorded a different growth pattern for ash. Ash EW shows an increasing trend over time, while oak EW shows certain trend similarities to LW and RW. We identified periods with growth releases and reductions for both species and all tree-ring components ( Figure 2). The first period with accelerated growth was identified during the juvenile period (the first 15-20 rings from the pith). After that period, the growth process levels lowered until the 1910s, due to competition. Between 1910 and 1940 a growth release was identified, more evident for oak than for ash. This period is overlapping with a new tree generation, with juvenile intense growth processes, possibly induced by a silvicultural intervention. After this growth release, both species have a normal negative trend, age-induced, more evident for oak ( Figure 2).
The inter-series correlation shows a high similarity of growth trends among individual trees, for RW and LW for both species, even if the sample depth for ash is not very high (e.g., for ash 0.728 RW/0.650 LW; oak 0.633 RW/0.590 LW), while EW indicates a growth incoherence in the datasets (0.330 for oak and 0.448 for ash). The variability explained by the first principal component decreases from 61.1% for ash RW to 47.1% for oak RW, the lowest values being recorded for EW (33.9%-ash, 21.8%-oak) ( Table 1). The agreement between the oak and ash RW series is highly significant (tVBP = 7.6, Glk = 70%), with a small decrease for LW (tVBP = 6.2, and Glk = 72%) and with minimum values recorded for EW (tVBP = 4.3, Glk = 60%). Most of the RW variability is induced by LW, showing that these two variables share the same information (tVBP = 50.4 for oak; tVBP = 52.6 for ash). The similarities between RW and EW are lower comparing with LW (tVBP = 5.1 for oak and tVBP = 7.1 for ash) (Figure 2). Year by year growth variation, expressed by mean sensitivity (MS) is higher for ash than oak, and for LW, than it is for RW and EW. The AC1 values, as an indicator of previous year environmental condition influence upon growth, are significant and higher for oak, compared to ash, and it is present in all tree ring width variables (RW, LW, EW) (Table 1).
Mean chronology quality statistics (EPS, %var) reveal an evident difference between studied species, being lower for oak compared with ash, for all tree ring component chronologies. The chronologies' statistical parameters are similar to other studies in Central and Eastern Europe, for oak and ash [14,33,36,68,69]. Besides the limitations induced by local climatic conditions, anthropic forcing (silvicultural interventions) and/or insect outbreaks can have a major impact on growth processes and forest dynamics. These non-climatic factors could cause synchronic changes in radial growth, increasing common signal and autocorrelation, but blurring the chronology climatic signal [69]. The running EPS values for ash are equal or higher than the 0.85 value, which is usually used as a threshold for the reliability of chronologies [57,70], indicating a strong and stable common signal for all ash tree ring width components (Figure 3). For oak, the EPS value decreases below 0.85 threshold around 1900 for EW, around 1930 for LW, and around 1920 for total ring width, pointing out a strong common signal after these periods. The obtained chronology statistics are similar to those from other studies on separate analyses of tree-ring components [68,69,71,72]. Overall, the dendrochronological series statistics suggest that EW and LW record different dendrochronological and climatic signals, while the RW signal relies on LW variability.

Correlation with Temperature and Precipitation
The present study provides valuable information that fills the knowledge gap regarding the climate-growth relationship of those two species in Eastern Europe. To quantify the climatic signal, we computed the correlation coefficients for all tree ring components of both species, with different monthly climatic parameters. The performed analyses reveal a general pattern characterized by a significant negative correlation with temperature and a significant positive correlation with precipitation for both species (Figure 4). The ash EW index is significantly negatively correlated with the minimum and mean temperature from August previous year (py) (r = −0.16; r = −0.21) and current May (r = −0.22 and r = −0.26) and with maximum temperature from the July-August-September py (r = −0.19), and current April and May (r = −0.23). Additionally, the ash EW is significantly positively correlated with precipitation from the July py (r = 0.37) and December py (r = 0.23). The ash LW and RW share similar climatic signal: negative correlations with maximum and mean temperature from May (r = −0.21) and positive correlation with precipitation from py October and December (r = 0.30; r = 0.25), current February, May, and July (r = 0.21; r = 0.21 and r = 0.27). The oak EW is significantly correlated with mean, minimum, and maximum temperature from the py October (r = 0.23). As it was found for ash, the oak LW registers a similar climate signal as RW, still, in oak's case, the correlation coefficients are lower for RW than for LW. The oak LW and RW is significantly negatively correlated with maximum temperature from July (r = −0.23, r = −0.19) and positively correlated precipitation from py December (r = 0.33) and current March-June, with the highest coefficient for June (r = 0.30) (Figure 4).
The obtained results indicate obvious differences in the climate response between ash and oak. As a general pattern, ash tree ring widths are more sensitive to climate than oak, for all studied climate variables, results consistent with similar studies in Europe [26,33]. The temperature during the vegetation period has a strong influence on all tree-ring components of ash, while for oak, the LW indicates the highest correlation values. High May temperatures for ash, and from July for oak, induces an increased transpiration rate, inhibition of chloroplast function, and stomatal closure [73]. These phenomena determine a photosynthesis reduction and radial growth decline, therefore a narrower EW, LW for ash, and LW in oak's case. The low climatic response of oak EW can be explained by the starting growth point of EW, before the bud burst [74]. A similar climatic response of the oak EW was recorded in different studies in Hungary [68] and Switzerland [69].
The climate-growth relationship analysis for ash shows, in general, a negative correlation with the previous summer temperature, while the oak response shows a positive correlation with temperatures from the previous autumn. These differences are associated with the physiological processes which affect the climate-growth relationship differently for both species. The ash negative correlation with previous summer temperature is induced by high evapotranspiration and respiration rates, which decrease the amount of carbohydrates. Likewise, the oak positive correlation with temperature from the last autumn represents the influence of carbohydrate reserves: a warm autumn could foster the accumulation of carbohydrates which will contribute to EW growth in the next spring [75]. In the ≈20 days between the earlywood growth starting point and the bud burst, up to 30% of EW width is already formed [22,76], thus earlywood growth in oak is more linked to pre-growing season conditions. Favorable autumn and winter conditions will have a positive effect on the earlywood formation process [77,78]. The usage of these reserves in the next spring is conditioned by vessel hydraulic capacity. If the previous EW vessels are affected by winter and spring cavitation [72,79], trees compensate with intensive production of new large EW vessels before leaf development, to recover the hydraulic architecture. This negative response to growing season temperatures is similar to others from Eastern Hungarian [25,68], NW Romania [23], and in the Alps [69,80]. The ash negative response to late spring and early summer temperatures was also reported by Koprowski, et al. [81] and Heklau, Jetschke, Bruelheide, Seidler and Haider [37].
The significant positive correlation between LW (RW) and precipitation for both species suggests that the hydrological component and precipitation are the main tree growth factors [82]. The water availability in the previous autumn and current growth season (May-July for ash and March-June for oak) leads to high photosynthetic rates, which determine a wider LW and, respectively, total ring width. Especially for the ash case, water deficit does not only affect directly the EW width but also impair indirectly the hormone concentrations [83]. Consequently, high auxin concentrations are linked to rapid cell differentiation which also affects cell development and EW width [71]. Additionally, ash EW development can be affected by severe winter-spring droughts or intense frost events [71]. Our findings regarding the oak RW/LW positive response to previous autumn and current spring to summer precipitation agree with other studies from Western [72], Southern [3,14,26,69], and Eastern Europe [24,25,68,84,85], where the water availability is considered the main driving factor for oak growth. Even if these oak trees are growing in a steppe environment, EW does not retain a significant response to precipitation, having a similar reaction with oaks in different environmental conditions from Europe [68,69].
Unlike oak, for ash, there is a scarcity of dendroclimatological studies in Europe, even though it has great dendroclimatological potential and ecological plasticity [26,33]. Nevertheless, similar pronounced sensitivity of ash to summer precipitation was reported in floodplains forests in Croatia [26], Central Germany [37], and Poland [81]. It is necessary to mention that, compared with these floodplain forests, in our region ash has a wide window of response to precipitation (from previous to current summer), as a consequence of water limitation (steppe climate) and soil conditions.

Correlation with the Drought Index
Analysis of the climate-growth relationship using a drought index (e.g., SPEI) has the advantage of combining the influences of the water deficit and temperature on tree growth into a single climate parameter. The obtained insignificant correlation for oak EW with the SPEI index, comparable to the other climatic parameters, confirms the low potential of the oak EW in dendroclimatological studies. Ash EW is sensitive to cumulative drought only on a time scale higher than 12 months. The correlation between LW and SPEI reveals distinct responses for ash and oak on both short and long term cumulative SPEI. For ash, the correlation begins to be significant only when the previous autumn conditions are included in the cumulative SPEI index. For oak LW, in addition to a similar response as for ash LW, we found a significant correlation with the current summer SPEI index, for cumulative periods higher than 3 months ( Figure 5). The ash and oak RW reflect a similar SPEI response as LW ( Figure 5).
Being a floodplain forest species, ash is well adapted to high levels of groundwater and it is negatively influenced by low soil humidity in the drought periods [26]. Ash response to long drought periods is in line with the general assumption that the species has a typical plate root system with endo-mycorrhizae [30], which allows exploitation of the upper horizons of the soil and being sensitive to decreasing soil humidity, a limitation set by the permanent groundwater level [86]. In dry sites, the ash water requirements are moderate, due to a lower maximum stomatal conductance and better control of stomatal activity [30] and due to elastic adjustments of cell walls, that can tolerate dehydration [29,87], a strategy similar to trees from dry sites [30]. Correlation between growth indices and monthly Standardized Precipitation-Evapotranspiration Index (SPEI) using different time scales (black line-95% significance level).
Unlike ash, oak has a deeper roots system with ectomycorrhizae [88]. The deep roots allow access to groundwater, while the fine roots and mycorrhizal hyphae utilize surface water infiltrated from heavy rain events during summer. In this way, oak can access groundwater and nutrients from deeper layers during long drought periods when the soil surface is extremely dry [88,89]. Several authors have shown that floodplain oaks forests, from the south-eastern part of Europe, were affected by the annual successive extreme drought events, which led to "a significant increase of sensitivity to increasing temperatures and decreasing river levels" [13,26,90]. As drought frequency will increase, tree species will become even more sensitive and this might lead to a general ecophysiological weakening of forest ecosystems. Although, the expected warmer climate will be, most likely, the first driver of growth decline, in species with creeping roots like beech and spruce [91,92], cases in which the absorbent fine roots are present in the top layer of the soil.

Temporal Stability of the Dendroclimatic Response
The seasonal climate growth relationship presents different temporal stability. The significant positive response of both species to spring precipitation at the beginning of the last century changes into a negative correlation in the last 40 years. The shift in the response is more evident for ash compared to oak ( Figure 6). Additionally, for oak EW, starting in 1960 appears a significant correlation with precipitation from the previous autumn. The significant positive influence of previous autumn temperature present in the first half of the 20th century has changed into a low-significance negative influence in the last decades for all tree ring components for both species except for oak EW, which does not present the significant correlations as usual. The LW and RW for both species present a strong and constant temporal stability to the SPEI index over the analyzed period. Changes in response patterns were identified in diverse conditions in Europe or as a result of severe drought periods [24,26,93]. As climate change intensified in the last decades, some trees' physiological boundaries may be exceeded and could induce temporal changes in dendroclimatic response patterns. The extreme warm springs and summers are characterized by very high vapor pressure and low precipitation amounts, which indicate high atmospheric humidity and low soil water availability. In these conditions, the vapor pressure deficit between leaves and air decreases, and trees reduce the transpiration rates and increase the CO 2 intake, through high stomatal conductance [94,95]. The soil nutrients play an important role in tree recovery after water stress periods. The phaeozem soil type has a high nutrient availability and this can increase water use efficiency thus minimizing negative feedback between carbon and nutrient balance [96]. Otherwise, pedological droughts induce soil compaction by decreasing soil porosity, aeration, and water infiltration capacity. These factors could lead to physiological dysfunctions in plants, influencing root development, making them unable to support physiological growth requirements [97], which could affect the temporal stability of the dendroclimatic pattern. Additionally, uncertainties induced by climatic data sets can obscure the dendroclimatic response [98], taking into account that, in the Republic of Moldova, there are few meteorological stations with short climatic records, which offer a low representativity in the gridded CRU database. The exogenous disturbance signals (like insects or fungi outbreaks, pollutants), although these factors were not observed in our data, can modify tree reactions to climate conditions [99,100]. Another reason behind the climate-growth response pattern might be due to the abrupt decrease in the snow cover in the last decades, over the analyzed region [101] and an increase in winter precipitation. A shift in the melt season date, due to less snow cover and more precipitation, can affect the initiation of cambial activity (necessary for the wood cells division and development). The authors of [102] have shown that delays in the snowmelt date, corroborated with increased winter precipitation can induce temporal changes in climate-growth response.

Stability Maps
Tree ring-based proxies (e.g., RW, MXD, stable oxygen, and carbon isotopes) are largely used to study the long-term climate variability [67,[103][104][105]. Nevertheless, one big challenge in dendroclimatological studies is the stationarity of the relationship between the tree ring proxies and climate-related variables [67,103,106,107]. Furthermore, a stable relationship between proxy-based data and climate is essential to develop further adaptative silvicultural measurements. In order to be able to test the stability, in time, of the relationship between our proxy data and climate-related variables, in this study, we computed the stability maps between EW, LW, and RW in oak and ash and PP, Tmax, scPDSI, and SPEI3 over the period 1902-2018. The basic idea of the stability maps is to identify regions where the correlation between the proxy data and the climate variables does not change over time. The oak EW does not show any stable and significant correlations with any of the analyzed variables. The oak LW shows positive stable and significant correlations with SPEI3 (scPDSI) from February until September over the eastern part of Europe (Figure 7 and Figure S1) and negative stable and significant correlation with the summer maximum temperature close to the location of our sampling area ( Figure S3).
Similar results (positive and stable correlations with SPEI3/scPDSI and negative and stable correlations with Tmax over the eastern part of Europe) are found also in the case of ash RW (Figure 8, Figures S2 and S4). One interesting aspect of the analysis of the stability maps for oak is that the stable correlations with scPDSI ( Figure S1) are extending over a larger area and throughout the whole year when compared with SPEI3 drought index (Figure 7), indicating that LW and RW in oak are very sensitive to the soil moisture conditions (a parameter used in the computation of scPDSI drought index). The sensitivity to the soil moisture conditions might be due to the fact that oak has very deep rooting systems which facilitate a good uptake of the nutrients and soil moisture even from the deep soil in conditions of a lack of precipitation, thus the soil moisture is a key element in the development of tree ring-based proxies with a deep rooting system.  In the case of ash, positive, stable, and significant correlations, throughout the year (January to September) are found for all the analyzed parameters: EW, LW, and RW (not shown). Ash LW and RW show also positive and stable correlations with spring (MAM) precipitation and spring (MAM) maximum temperature in the eastern part of Europe. A general outcome of the stability maps analysis is that both oak and ash respond stably and significantly to SPEI3 drought index, over the eastern part of Europe. The response to maximum temperature is seasonally dependent and just LW and RW show significant and stable correlations with the maximum temperature.

Conclusions
In this study, we developed and presented the first differentiated earlywood and latewood oak chronologies for the Eastern part of the Republic of Moldova, and one of the first differentiated ash chronologies in Europe. This study allows us to cover the knowledge gap of temporal stability and the climatic response of oak and ash over the analyzed region. The differentiated analyses show that the ash EW records a different climatic signal compared to LW, while the oak EW does not register a significant climatic signal. The RW, for both ash and oak, shares a similar climatic response as LW.
Analysis of the climate-growth relationship reveals a significant negative correlation with the mean temperature and a significant positive correlation with precipitation and SPEI drought index for both ash and oak tree ring width components. Despite the significant correlation with precipitation and temperature for the whole period, the 25-year moving correlation analyses show that they are not stable in time and can switch from positive to negative or vice versa, while the correlation with SPEI drought index, which is a reflection of both climatic parameters, is stable over time.
Based on the stability map analyses, we show that oak (and ash) tree ring components from the eastern part of the Republic of Moldova have a stable and significant correlation with SPEI3 and scPDSI drought indices from February (January) until September, over the eastern part of Europe. The correlation between oak LW and scPDSI is extended over a larger area throughout the whole year when compared with the SPEI3 drought index, indicating that oak LW is very sensitive to the soil moisture conditions (a parameter used in the computation of scPDSI drought index). Additionally, ash LW shows positive and stable correlations with spring (MAM) precipitation and spring (MAM) maximum temperature in the eastern part of Europe, and oak LW shows a negative, stable, and significant correlation with the summer maximum temperature close to the location of our sampling area. The response to maximum temperature is seasonally dependent and just LW and RW show significant and stable correlations with the maximum temperature.
The different, but high sensibility of the oak and ash tree species to long term droughts events, which directly affect the tree growth, can be used as an early-warning sign of the necessity to adopt proper forest management plans and strategies, which are crucial to increase forest resilience and resistance to upcoming future extreme events.