RESTRICTRING CLIMATIC CONDITIONS ON THE EASTERN .

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https://doi.org/10.15551/pesd2019132002PESD, VOL. 13, no. 2, 2019RESTRICTING CLIMATIC CONDITIONS ON THEEASTERN DISTRIBUTION LIMIT OF EUROPEAN BEECH(FAGUS SYLVATICA) IN NORTH-EASTERN ROMANIAFOR THE MARCH – JUNE INTERVALDumitru Mihăilă1*, Andrei Emil Briciu1, Cătălin ConstantinRoibu2, Petruţ Ionel Bistricean1&3**Key words: restrictive climate, eastern beech limit, north-eastern Romania,pluviometric deficit, growth indexAbstract: The meteo-climatic arguments for the eastern biogeographic limit ofbeech in Romania are of particular interest to forestry, but also to geographersand climatologists. This limit marks the transition from the temperate humidclimate of Western and Central Europe to the temperate continental climate ofEastern Europe. Our paper provides improved knowledge on climaticconditions that restrict the longitudinal distribution of beech at temperatelatitudes in north-eastern Romania. Results show that rainfall scarcity and hightemperature in the March-June interval, added to temperature drop below thefreezing point in April-June are the main climatic conditions that limit beechexpansion eastward of this biogeographic limit.IntroductionThe transition between Suceava and Bârladului plateaus and MoldovaPlain is characterized by a gradual, eastward change from forest to foreststeppe and steppe.In this region, European beech (Fagus sylvatica) occurs at the easternlimit of its natural distribution. Although old and vigorous beech trees arefrequently found in the forests of this area (e.g., a 417-year-old beech-tree wasidentified in the Humosu - Iași Reserve; Roibu, 2010, Roibu, et al., 2017), thespecies is subject to restrictive climatic conditions specific to north-easternRomania.Temperature drop below the freezing point at the beginning of theannual vegetation growth cycle negatively affects beech growth rings.1Departmentof Geography, “Stefan cel Mare” University of Suceava, RomaniaBiometrics Laboratory, “Stefan cel Mare” University of Suceava, Romania3Regional Meteorological Center of Moldova, National Meteorological Administration, Romania*email: dumitrum@atlas.usv.ro; **petricabistricean@gmail.com2Forest

18 Dumitru Mihăilă, Andrei Emil Briciu, Cătălin Constantin Roibu, Petruţ Ionel BistriceanFurthermore, high temperatures favour increased evapotranspiration and have anegative effect on the growth and expansion of this species.Water scarcity, manifested as drought, raises many economic andecological issues (Mihăilă, 2006, Nedealcov, 2012). In this part of Europedrought occurs with increased frequency and duration, making the territoriesvulnerable (Alexandrov et al., 2010). The thermo-pluviometric prognoses showan increase in water shortage particularly during the vegetation season (Potop,2011, Piticar et al., 2016, Mihăilă et al., 2017).Dry and very hot summers and autumns are more frequent (Boroneanţ etal., 2013) and generally followed by cold, unstable winters with short-livedsnow cover. Water shortage during the vegetation season leads to a lowerbioaccumulation in forest ecosystems, which also lose their vitality (Dobbertin,2005). Water shortage acts as a limiting factor on the eastern natural limit ofbeech. Beech development is optimum under temperate and wet climaticconditions and this species becomes increasingly sensitive to drought, as theclimatic conditions at the limit of its eastern distribution area change (Bréda etal., 2006, Nahm et al., 2006, Kramer et al. 2010, Piticar et al., 2016, Mihăilă etal., 2017).Dendrochronological research on beech trees has shown a positivecorrelation between the annual ring width and precipitation amount of thevegetation season (Dittmar et al., 2003, Fotelli et al., 2009, Roibu, 2010, Roibuet. al, 2017, Scharnweber et al., 2011).The relationship between water shortage and tree radial growth is basedon the monthly or seasonal precipitation amount (Michelot et al., 2012,Lebourgeois et al., 2005, Scharnweber et al., 2011).Precipitation variability, characteristic of the areas with a continentaltransition climate, requires that the analysis of the temporal relationshipsbetween tree growth and moisture availability should be based on syntheticclimatic indices at different temporal scales (Vicente-Serrano et al., 2012).The Standardized Precipitation Index (SPI) has the ability to highlightthe duration and intensity of precipitation deficit at different time scales(McKee et al., 1993). Rainfall deficit and high temperatures accentuate thenegative consequences of climate on physiological processes of trees andaccumulation of woody biomass. The standardized precipitationevapotranspiration index (SPEI) integrates potential evapotranspiration intorainfall deficit and can be successfully used in the climate-tree relationshipanalysis (Vicente-Serrano et al., 2010, Popa, Caisîn, 2015).Chira et al. noted in 2003 that beech decline occurred over successivedrought years. Analysis of the de Martonne climatic index for the last 40 years

Restricting climatic conditions on the Eastern distribution limit of european beech (Fagus sylvatica)19indicated an increase in the frequency and duration of drought in the forest beltof the Suceava hilly area.Chira et al. (2005) showed that the 1999-2000 drought was strongly feltin the eastern and north-eastern part of Romania and contributed, along withother climatic factors, to the phenomenon of beech debilitation (drying) in theold-growth (over 100 years old), pure and highly productive forest stands.Other climatic factors including late frosts and hail weaken the resistance ofbeech (large hail causes growth similar to beech cancer) and favour theoccurrence of Nectria infections (Chira et al., 2005).Negative correlations with high temperature during the vegetationseason were also noted. Climate warming is considered a promoting factor forbeech debilitation (Chira et al., 2005).1. Study areaThe eastern limit of the distribution of beech forests in north-easternRomania overlaps the contact line between the Moldova Plain and the SuceavaPlateau in the west, the Bârlad Plateau in the south respectively. Practically,this diffuse or transition area between forest and forest-steppe is largelyidentified in the physical-geographic contact subunits between the Moldovahilly plain and the two plateau areas (Suceava in the west, Bârlad in the south),which are known in the Romanian geography under the name of cuestas:Ibănești Cuesta (located in the north of the Moldova Plain), Moldavă Cuesta(between Moldova Plain and Suceava Plateau) and Iași Cuesta (betweenMoldova Plain and Bârlad Plateau). Due to specific physico-geographic andsocio-economic conditions, only patches of compact beech forests can still befound today in this area, particularly on higher elevation, more isolatedlandforms.The mathematical position in terms of latitude (the study area is locatedbetween 48 15'N and 47 N) and longitude (25 4'E - 27 55'E), along with itsgeographical position within Europe (in the centre of the continent, with lowoceanic influences) and Romania (north-eastern part) shape the climate of thestudy area with temperate (annual mean global radiation on a horizontalsurface is around 115 Kcal/cm2; the existence of four seasons) and transitioncharacteristics (from the oceanic climate, which becomes increasingly evidentas we move westward from the Eastern Carpathian Mountain range, to thecontinental climate, typical of Eastern Europe; from the sub-Mediterraneanclimatic influences frequent in the southern parts of Romania, to the Baltic andboreal characteristics often present in northern Romania).- Permanent, semi-permanent or seasonal high-pressure (e.g., AzoresHigh, Siberian High, Scandinavian-Baltic High, Greenland High) and low-

20 Dumitru Mihăilă, Andrei Emil Briciu, Cătălin Constantin Roibu, Petruţ Ionel Bistriceanpressure atmospheric systems (e.g., Icelandic Low, Mediterranean Low,Eurasian Low) impose a high degree of variability on climatic elements(especially temperature, precipitation, wind parameters) and phenomena, afeature specific to climates with an enhanced degree of continentality.- Among the regional and local background features of the studied area,the following are climatically relevant:a) Eastern Carpathians, which form an orographic barrier in the directionof wetter air masses coming from Western Europe; oceanic air masses generaterain on the western slopes of the Eastern Carpathian range and foehn on theeastern slopes towards Suceava Plateau and Moldova Sub-Carpathians (theaverage difference in elevation between Obcina Mare Peaks and SuceavaPlateau is 800 - 1000 m a.s.l.);b) the study area is widely open towards north, northeast and east, in thedirection of Baltic, Nordic and Continental air masses (main river valleys andmountain ranges are arranged northwest - southeast, which facilitates theadvection of air masses from NW and SE);c) the elevation difference of 150-300 m between Suceava / Bârladplateaus and the Moldova Plain, evident in the transition area between the twolandform types (the northern, western and southern hilly marginal cuestas ofthe Jijia Plain), which favors a second foehnization (of lower intensity butrelevant with regard to rainfall occurrence) of the western air masses in theiradvection towards eastern Europe.Next to their role in precipitation distribution patterns, the twoorographic barriers block winter and spring advections of polar continental airmasses towards western Europe, thus enhancing frost in the lowlands of northeastern Moldova and favoring prolonged thermal inversions and a longerpersistence of the snow layer. In summer, under relative shelter conditions,temperature in the lower elevation areas of the Moldova Plateau reaches andfrequently exceeds the heatwave threshold.All these climatic conditions impose thermal and pluviometricrestrictions on beech growth, which lead to a precarious balance in the propersuccession of phenophases in the species, with more profound and frequentsyncopes towards the east. This leads to increasingly unfavorable conditionsfor beech expansion in an increasingly continental climate.2. Data usedThe data from 13 meteorological stations and 57 pluviometric stations(Figure 1 and Table 1) were used to depict the climatic conditions for beechgrowth in the study area. Additional wood cores were extracted from beechtrees in 6 dendrocronological series (Figure 1 and Table. 2).

Restricting climatic conditions on the Eastern distribution limit of european beech (Fagus sylvatica)21In order to understand the relationship between beech growth andclimate on the eastern limit of the natural distribution for this species, 81 treeswere sampled (13-33 samples / site) in 2005. 12 series were removed from theanalysis due to their short length, low correlation with the mean series or crossdating problems due to false annual rings (Dittmar et al., 2003, Roibu, 2010,Roibu et al., 2017). More methodological details are presented in Roibu, 2010and Roibu et al., 2017.Figure 1. Geographic location of the eastern natural distribution limit of beech innorth-eastern Romania; filled circles show the position of meteorological, pluviometricand dendrochronological series where data was obtained for climate characterization.The meteorological data for climatic parameters relevant to theecological conditions of beech growth span the 1961-2010 time interval; otherparameters such as trends in climatic variables or water balance are availablefor a longer interval, i.e., 1961-2017.

22 Dumitru Mihăilă, Andrei Emil Briciu, Cătălin Constantin Roibu, Petruţ Ionel BistriceanTable 1. Attributes (station code, name, mathematical coordinates and elevation) of themeteorological and pluviometric stations in north-eastern Romania located near theeastern beech limit.

Restricting climatic conditions on the Eastern distribution limit of european beech (Fagus sylvatica)23Table 2. Attributes (station code, name, the mathematical coordinates and elevation) ofthe dendrochronological series for stations located on the eastern beech limit in northeastern Romania. Details of the relationships between beech growth and climate, asrevealed by the dendrochronological series (extracted from Roibu, 2010).Average length oftree-ring samples(years)Time span (years)Average radialgrowth (mm yr-1)First-order averageautocorrelation forradial growth seriesAverageautocorrelation forstandard growthindices seriesAverageautocorrelation forresidualdendrochronological seriesDolheștiSeriesDOFS47.418161N26.52796 E450 m a.s.l.Dragomirna SeriesDRFS47.786521N26.22032469 m a.s.l.HumosuSeriesHUFS47.498898N26.72381 E456 m a.s.l.Ruja SeriesRJFS47.319427N26.59739 E450 m a.s.l.StuhoasaSeriesSHFS48.158761N26.36752 E214 m a.s.l.Trei PietreSeriesTRFS47.515159N26.70764 E483 m a.s.l.112 24(101-147)110 16(96-135)257 98(154-416)156 3(145-156)108 15(93-146)76 37(60-178)1831-20080.71 0070.71 – 6.470.34 – 5.020.16 – 4.110.32 – 5.940.38 – 7.720.64 0.190.64 0.140.61 0.160.57 0.100.66 0.060.72 0.120.38 0.200.36 0.120.44 0.180.46 0.100.36 0.060.60 0.18-0.02 0.060.00 0.01-0.02 0.060.00 0.010.01 0.050.04 0.07Growth indices series average 2σ1982, 19971970,1982,1988,1997, 20011961, 1970,1975, 1982,19901966, 1970,1975, 1982,19981982, 1988,1997, 20011975Growth indices series average - 2σ1964, 1968,19831964,1968,1972, 19831964, 1968,1987, 1995,2000, 2003,20071964, 1968,1987, 19961964, 1968,1995, 2000,20031972, 19873. MethodsAn 81 trees were sampled in 2005 (13-33 samples/site). The growthseries were standardized to remove the biological trend and to maximize theclimatic signal. Residual growth indices were used to quantify the climate-treerelationship (Roibu et al. 2017). For each site, we used monthly averageprecipitation measured at the nearest meteorological/pluviometric station,spanning the 1961-2005 interval. Correlations and relationships were derivedbetween biometric indices and climatic parameters which contribute in varyingproportions to the water balance matrix available for beech growth.The current eastern limit of beech growth in north-eastern Romaniashows some interesting climatic peculiarities for the interval March-June,which are important because during this interval beech is very sensitive to

24 Dumitru Mihăilă, Andrei Emil Briciu, Cătălin Constantin Roibu, Petruţ Ionel Bistriceanweather conditions. These climatic characteristics were more thoroughlyapproached through case studies, to depict the climatic reality relevant forbeech growth. We synthesized the temporal trends in temperature andprecipitation, as resulting from climatic data. All these analysis approachesrevealed key climate features influencing beech growth in the study area.The growth indices were correlated with March-June (M-J) air/soiltemperature and precipitation spanning the 1961-2005 interval. Studies haveshown that this period of the year is of particular relevance to climaticrequirements of beech (e.g., Roibu, 2010, Roibu et al., 2017). On the easternlimit of beech distribution in north-eastern Romania, statistically significantnegative coefficients were obtained between temperature drops below 0 C inthe April-June (A-J) interval and the dendroclimatological response of beech;conversely, statistically significant positive coefficients were obtained betweenprecipitation amounts in the M-J interval and beech response. Water deficiencyin the M-J interval can influence significant the growth processes. Correlationsand relationships were thus derived between growth indices and climaticparameters that contribute in varying proportions to the heat balance and wateravailability matrix for beech growth.Temperature and precipitation maps were constructed during 3 majorstages using known GIS techniques. We used the data from 11 stations for soiltemperature, 13 for air temperature and 69 for precipitation. Ordinary kriginginterpolation was one of the methods used. Kriging has also been usedsuccessfully in other meteorological studies (Venkatram, 1988, Boer andLambert, 2001, Alsamamra et al., 2009).4. ResultsMany studies have already shown that beech is strongly influenced byclimatic factors (temperature and precipitation). For north-eastern Romania,Roibu (2010) and Roibu et al. (2017) demonstrated that temperature andprecipitation in the M-J interval of each year are very important for theecological cycle of this species (Table 3).The present study also focuses on the M-J time interval of the year, alsoconsidering the temperature-precipitation interaction from the second half ofthe previous year, which is very important for the bioaccumulation process inbeech species, for its territorial distribution respectively.Average monthly temperature. In the M-J interval, average soil surfacetemperature increased from 1.1 and 3.2 C in March at Rădăuţi and PoduIloaiei, to 20.5 and 24.5 C in June at Rădăuţi and Podu Iloaiei respectively Figure 2a, with a mean thermal jump of over 20.1 C.

Restricting climatic conditions on the Eastern distribution limit of european beech (Fagus sylvatica)25Similarly, the average monthly air temperature (Figure 2b) increasedfrom 1.3 C in March at Rădăuţi, 3.1 C at Podu Iloaiei and Iași respectively, to19.5 C in June at Podu Iloaiei, with a mean thermal jump of 16 C, i.e., 4 Clower than the thermal jump on the soil surface.Table. 3 Correlation coefficients between tree ring index and main climatic parameters(extracted from Roibu et al., 2017).DendroseriesmjjPrevious DOFSSTFS-0.29 -0.24-0.30-0.26 -0.29 -0.22 -0.24-0.25 -0.39-0.19-0.29-0.29-0.23 -0.24 -0.260.370.26ondJPrecipitation0.270.210.210.23Mean temperature0.240.210.25FMCurrent .27250.22-0.27 -0.31-0.32-0.37-0.32-0.22-0.38-0.25-0.33On a monthly basis, the average temperature in the M-J interval showsslight increases (3 - 6 C for soil surface, 3-4 C for air) both in the NW-SE andW-E directions (2 - 3 C for both soil surface and air) – Figure 3a-b; 4a-b.Figure 2. Variability of average monthly a) soil surface and b) air temperature(March - June) on the eastern beech limit and the surrounding area (1960-2010).Abbreviations in the figure refer to measurement stations included in Table 1.These situations can be explained by the decrease in elevation from NWand W towards SE and E, and also by the changes in the active surface

26 Dumitru Mihăilă, Andrei Emil Briciu, Cătălin Constantin Roibu, Petruţ Ionel Bistriceancharacteristics (reduction of the forest cover, increase in the areas covered byforest-steppe and steppe vegetation etc.)Figure 3 Spatial distribution of average soil surface temperature in a) March, b) June.These situations can be explained by the decrease in elevation from NWand W towards SE and E, and also by the changes in the active surfacecharacteristics (reduction of the forest cover, increase in the areas covered byforest-steppe and steppe vegetation etc.).Temperature jumps on both soil surface and air (20º and 16ºCrespectively) show that the phaenological stages of beech are forced to developfaster than in cooler climates with moderate temperature differences.Highest maximum temperature analyzed annually for the M-J interval.The maximum soil surface temperature in the study area was 36.0ºC in Marchat Rădăuţi, and 65.0ºC in June at Iași. The average temperature jump of themonthly maxima in soil surface temperature in the M-J interval was around20 C (from 40.4 C in March to 59.9 C in June). Conversely, maximum airtemperature was between 24.3ºC in March at Suceava and 36.4ºC in June atDorohoi. For thermal jumps in air temperature, the increase is less prominent(from 25.5 C in March, to 35.2 C in June). Such high amplitude jumps in soiland air temperature are not beneficial for beech growth.

Restricting climatic conditions on the Eastern distribution limit of european beech (Fagus sylvatica)27a.Lowest minimum temperature analyzed annually for the M

Dumitru Mihăilă, Andrei Emil Briciu, Cătălin Constantin Roibu, Petruţ Ionel Bistricean 22 Table 1. Attributes (station code, name, mathematical coordinates and elevation) of the meteorological and pluviometric stations in no

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