Tree-ring variation, wood formation and phenology of beech (Fagus sylvatica) from a representative site in Slovenia, SE Central Europe
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- Čufar, K., Prislan, P., de Luis, M. et al. Trees (2008) 22: 749. doi:10.1007/s00468-008-0235-6
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Long-term variation in tree-ring widths (1873–2006) and intra-annual dynamics of cambial activity and tree-ring formation in 2006 were studied in mature beech (Fagus sylvatica L.) trees at a typical forest site near Ljubljana (46°N, 14°40′E, 400 m a.s.l.) and related to leaf phenology and climate data. Tree-ring widths were negatively affected by minimum March and maximum August temperatures and favoured by May and July precipitation. Precipitation of the previous August and temperature of the previous November also had a positive effect. Leaf unfolding was affected by March and April temperatures, occurring later if they were low. Leaf yellowing was positively affected by minimum July temperatures and negatively by September precipitation. In 2006, leaf unfolding occurred on 16 April and was immediately followed by reactivation of cambium at breast height of the trees. One week later, the cambium obtained its maximum width (around 11 cell layers) and the rate of division increased until the end of May/beginning of June. By the end of June, 75% of the tree-ring was formed. Cambial cell divisions stopped from the end of July to mid-August. The average time of cambial activity was 100 days. Leaf yellowing occurred at the end of October, i.e. nearly 2 months after the cessation of cambial cell division. We discuss the usefulness of a combination of long-term (tree-ring width and phenology) and short-term (wood formation at a cellular level) data to understand better the environmental signals registered by a tree during growth.
KeywordsEuropean beech = Fagus sylvaticaWood formationTree-ringsClimatePhenology
European beech (Fagus sylvatica L.) is among the most important forest species, with an ability to grow on a great variety of sites all over Europe (Mayer 1984). Its proportion is currently increasing in Central Europe, particularly where forests with a high percentage of conifers are being converted into more natural mixed forests (e.g. Tarp et al. 2000; Bončina et al. 2003). It has recently been reported that the competitiveness of beech might be considerably reduced due to climate change (Geßler et al. 2007). At the edge of its southern range, the changing climate may even cause a retreat of beech populations (Jump and Peñuelas 2006). Similar observations have been made in Slovenia, SE Central Europe, where beech is the basic structural element of most forest associations from the lowlands up to the high mountains (Marinček 1987) and forms more than one-third of the wood stock (Brus 2005). The climate change scenario for this region predicts a rise in temperature and more uneven distribution of precipitation associated with more frequent droughts and extreme rainfall events (Bergant and Kajfež-Bogataj 2005), which might affect the survival of beech, particularly on more extreme and marginal sites (Diaci 2007).
Because of its frequency, ability to grow on sites of wide ecological variability and its longevity, beech is well-suited for assembling spatial networks of tree-ring chronologies. The beech can be used for dendroecological studies, especially to evaluate the growth and climate relationships in different bioclimatological units, and to estimate future prospects and possible ecological risks associated with climate change (e.g. Eckstein et al. 1984; Gutierrez 1988; Biondi 1992; Rozas 2001; Dittmar et al. 2003; Piovesan et al. 2005; Lebourgeois et al. 2005; Di Filippo et al. 2007). Most dendroclimatological studies are based on analyses of tree-ring widths that integrate positive and negative environmental influences affecting the growth of a tree during the current or previous years (Eckstein 2004). The application of densitometry showed that within and between year density variations in beech provide more information at higher temporal resolution, than tree-ring widths only (Z’Graggen 1992; Bouriaud et al. 2004; Skomarkova et al. 2006). Analysis of wood structure provides even better resolution, since the morphology of the cells records the effects of different factors on a finer time scale during the time of wood formation (Eckstein 2004; Frankenstein et al. 2005). Studying the time series of vessel areas in beech wood showed that they can be used as an ecological variable indicating the impact of internal and external factors on the process of wood formation (Sass 1993; Sass and Eckstein 1995). However, if we want to understand the information on factors affecting wood formation recorded in the wood structure we need to identify which signal (and to what degree) affects a particular feature in the wood (e.g. Fonti et al. 2007).
For this purpose, studies on wood formation during the growth season are needed. Studying wood formation on a cellular level requires destructive sampling from living trees and time consuming preparation and measurement of microscopic sections (e.g. Gričar et al. 2007). This is among the main reasons that wood formation in beech has, to our knowledge, only been studied in northern Europe for one or two seasons (Schmitt et al. 2000; Werf van der et al. 2007). In northern Germany, wood formation data were combined with phenological data (Schmitt et al. 2000) and in the Netherlands with long-term tree-ring and climate data (Werf van der et al. 2007). Such combinations of data proved to be useful for explaining the environmental signals registered by a tree during different phases of wood formation.
In the SE part of Central Europe, detailed intra- and inter-annual studies of wood formation in relation to climate are still lacking in deciduous tree species. We therefore decided to study adult beech trees from a typical forest site near Ljubljana. The objectives of the study were: (1) to evaluate long-term intra-annual tree-ring characteristics and leaf phenology in relation to climate variation; and (2) to present the dynamics of cambial activity and tree-ring formation on a cellular level in the 2006 growth period. We discussed the obtained results in the context of climate change predictions.
Materials and methods
Study site characteristics
The study was carried out at a forest site Panška Reka near Ljubljana (approximately 46°N, 14°40′E, 400 m a.s.l.). The privately owned forest site belongs to the Blechno fagetum forest association. The predominant tree species in the site is beech (F. sylvatica L.).
Tree selection and sampling
During winter 2005–2006, 14 isolated, dominant or co-dominant, healthy beech (F. sylvatica L.) trees with diameter 40–50 cm, height 25–30 m, and ages above 100 years were selected for analysis. Six of them were visited at weekly intervals from April until September 2006 to collect intact tissue samples in order to study cambial activity and growth ring formation on a cellular level. Thereafter, during winter 2006–2007, all the 14 trees were felled and the stem discs were taken for tree-ring analysis.
Intact tissue samples
Samples (25 × 10 × 10 mm) were taken from the breast height (1.3 m) of six living trees with a chisel and knife. They contained phloem, cambium, developing and older outer xylem. They were fixed in FEA (formalin–ethanol–acetic acid solution), reduced to blocks of dimensions 2 × 2 × 3 mm, dehydrated in ethanol and embedded in paraffin (Rossi et al. 2006a). Cross sections of 12-μm thickness were stained with safranin (0.5% in 95% ethanol) and astra blue (0.5% in 95% ethanol) and observed under a Nikon Eclipse 800 light microscope (bright field and polarized light) and analysed with a Lucia G 4.8 image analysis. We examined the cambium (number of cells along three radial files and the width in μm) and the current xylem growth ring (increment width in μm along three radial lines).
Tree-rings and chronology computation
The discs taken from 14 trees felled in winter 2006–2007 were polished and the tree-ring widths were measured to the nearest 0.01 mm. The TSAP/X program was used for data acquisition. The tree-ring series were visually and statistically cross-dated and compared with each other by calculating the t value after Baillie and Pilcher (1973) using TSAP/X and TSAP-Win.
The tree-ring series were assembled in a local chronology using the ARSTAN programme (Holmes 1994). The individual raw tree-ring series were hereby standardized in a two-step procedure. First, the long-term trend was removed by fitting a negative exponential function or a regression line to each tree-ring series. Second, a more flexible detrending was made by a cubic smoothing spline with a 50% frequency response of 60 years, in order to reduce further non-climatic variance. Thereafter, autoregressive modelling of the residuals and bi-weight robust estimation of the mean were applied (Cook and Peters 1997). We then made three versions of the chronology, a non-detrended raw-data, a detrended standard, and a detrended residual chronology for analyses of the tree-ring and climate relations.
Phenological data (the date of leaf unfolding and the date of general leaf yellowing) for beech from the site in Ljubljana were obtained from the Environmental Agency of the Republic of Slovenia (Črepinšek and Zrnec 2005). The period of observations was 1960–2006.
Climatic data (minimum, maximum and mean monthly temperatures and monthly amount of precipitation) for the period 1960–2006 were obtained from the Ljubljana climate station (299 m a.s.l., 46°04′N,14°29′E) of the Environmental Agency of the Republic of Slovenia. The station is located approximately 10 km from the forest site.
Climate–growth and climate–phenology relationships
Climate–growth relationships were calculated using the program DendroClim2002 through correlation function analysis (Biondi and Waikul 2004), where the residual version of the tree-ring chronology was the dependent variable and the regressors were the monthly minimum, maximum and mean temperatures and the monthly sums of precipitation for each year from the previous August to the current November. The program applies a bootstrap process (Guiot 1991) to assess the statistical significance of the correlation coefficients.
The influence of climate on the three phenological variables used (date of leaf unfolding, date of general leaf yellowing and the time span between these two dates, indicating the period when the trees had active leaves) was estimated using forward stepwise regression techniques with the same climate regressors.
Interannual tree-ring formation
Xi is the average width of xylem growth ring 2006, i is the date of sampling; n is the number of measurements, j is the subsequent measurement on individual sample.
Inter-annual variability in tree-rings and phenology
Descriptive statistics for chronologies (raw, standard, residual) of beech (Fagus sylvatica) from Ljubljana, Slovenia, for the period 1960–2006
Raw non-detrended chronology
Residual (AR 1)
Mean ring width (mm)
Mean correlation between trees
Agreement with population chronology
After standardization, the ARSTAN standard chronology still showed a significant first order autocorrelation; the residual chronology was therefore calculated by autoregressive modelling, which showed no significant autocorrelation between tree-ring indices. The main descriptive statistics of the chronologies are presented in Table 1. The obtained chronologies and their replication are shown in Fig. 3a, b.
Phenology of leaf development in beech in Ljubljana in the period 1960–2006
Year 2006 DOY
Ns (r2 = 0.003; df: 1, 45; F = 0.131; P = 0.719)
Ns (r2 = 0.057; df: 1, 45; F = 2.723; P = 0.106)
Days with leaves
Ns (r2 = 0.037; df: 1, 45; F = 1.743; P = 0.193)
Effects of climate on tree-ring formation and phenology
Stepwise regressions (r2) for influence of climate on phenological variables, FL general leaf unfolding, LY leaf yellowing, and DwL days with leaves
Wood formation dynamics in 2006
The combined information obtained from a more than 100-year tree-ring chronology, 46-year-long leaf phenology series, the seasonal dynamics of wood formation in 2006 and its relation to climate, enabled us to present the milestones of wood formation, as well as the main climate parameters that affect year to year tree-ring variation and phenology (leaf unfolding and leaf yellowing) for beech near Ljubljana. These milestones are presented in Fig. 8 and are discussed below.
We observed a close correspondence between leaf unfolding and reactivation of the cambium. The two processes occurred at almost the same time, on 16 and 18 April (DOY 106 and108) 2006, and were slightly earlier than the average leaf unfolding date for the period 1960–2006, which is 20 April (DOY 110) (Table 2). This confirms earlier reports that leaf unfolding can be used for a rough estimate of the onset of cambial divisions and that cambium reactivation takes place immediately after bud breaking in beech as a diffuse porous species (e.g. Bosshard 1974; Panshin and de Zeeuw 1980; Suzuki et al. 1996; Schmitt et al. 2000).
Climatic conditions in March and April proved to affect the time of leaf unfolding. In the study area, minimum April temperature is on average 5.1°C although in particular years it can be lower than 3°C or higher than 8°C; in 2006 it was 6.3°C. Such inter-annual variations in temperature cause a variation in the time of leaf unfolding. It is delayed if the temperatures are lower or anticipated if the temperatures are higher. The effect of temperatures on leaf unfolding in beech has also been shown in other studies (e.g. Črepinšek et al. 2006; Dittmar and Elling 2006). Variability in March–April minimum temperatures therefore seems to play an important role in defining the beginning of the growing season and it could indirectly affect the final tree-ring width.
The rate of cell divisions was low in the first weeks after cambial reactivation and maximal at the end of May–beginning of June, i.e., more than 1 month after reactivation of the cambium. Correlations with climate indicate that May precipitation affects year to year tree-ring variation and that the tree-rings were wider when May was wet. It is likely that precipitation in May has both direct and indirect effect on growth, the latter due to affecting the amount of available water in summer, which also depends on the water storage capacity of the soil (e.g. Bouriaud et al. 2004).
June can be considered the most important month for tree-ring formation. In June 2006, we observed the highest monthly amount of wood production, when approximately 35% of the entire tree-ring was formed. The average mean June temperature in the study area is 18.4°C, with an average maximum of 24.2°C and average minimum of 12.9°C. June is also the month with the highest average sum of precipitation in the study area (143 mm). However, June 2006 was characterized by below average precipitation and slightly higher temperatures than the long-term average.
The maximum weekly production of wood occurred between 30 May and 6 June 2006, which is more than 2 weeks before the summer solstice (21 June). The importance of June and the summer solstice with the longest photoperiod, has been described for conifers from various sites in North America and Europe (Rossi et al. 2006b; Gričar 2007), whereas maximum cell production in deciduous species proved to take place earlier, i.e., at the end of May (Eschrich 1995; Marion et al. 2007).
During July, cambial activity in investigated beech trees gradually decreased and the cessation of cell division took place from late July to mid–August 2006. Numerous similar studies on various conifers from the temperate climatic zone have shown that cambial activity stopped at the latest by the end of August (e.g. Antonova and Stasova 1993; Horacek et al. 1999; Schmitt et al. 2004; Rossi et al. 2006b; Gričar 2007). On the other hand, the wood formation in beech in the Netherlands ended in October (Werf van der et al. 2007) and in northern Germany in September (Schmitt et al. 2000). Similarly, Marion et al. (2007) found that cambial activity in Norway maple in Ljubljana continued until the first part of September. Bouriaud et al. (2004) reported that the radial increment in beech trees stopped quickly, or was greatly limited when a soil water deficit occurred.
We assume that maturation of the latest formed latewood cells continued after the cessation of cambial activity, as also observed in several studies on different tree species (Whitmore and Zahner 1966; Gindl et al. 2000; Gričar et al. 2005; De Luis et al. 2007).
After the cessation of cell division in the cambium, the trees retained active leaves capable of photosynthesis for two more months, until 21 October 2006. General leaf yellowing in 2006 occurred 3 days later than the long-term average. The products of photosynthesis in the period after the cessation of cambial activity were probably accumulated as reserves in storage tissues. This may explain the effect of the climate of the previous year on current tree-ring width. We namely observed a positive effect of previous August precipitation and previous November maximum temperatures on tree ring width.
Our study, showed no relation between the time when the trees had leaves and ring widths. We also demonstrated that leaf unfolding, leaf yellowing, time with leaves and ring formation, are linked to different climatic effects.
Climatic conditions on the study site are apparently optimal for the growth of beech. This explains the relatively low mean sensitivity, which was 0.14 for raw and standard chronologies, and 0.17 for residual. These values are lower than, at several sites in Italy, Austria, and Slovenia (Di Filippo et al. 2007) or in other European sites (Dittmar et al. 2003) where the climate is possibly more limiting for growth and thus explains the higher amount of year to year variation in tree-ring widths.
It should be noted that June 2006 was extremely dry, with only 46 mm of precipitation (compared to 143 mm long-term average) and July was extremely hot, with absolute maximum values of monthly mean, minimum and maximum temperatures in the period 1960–2006. Hot and dry June and July conditions are in agreement with climatic change predictions for Slovenia (Bergant and Kajfež-Bogataj 2005), so climate change might affect the productivity of beech. Reduced productivity, competitiveness, and survival chances of beech on more extreme sites have already been observed in the Mediterranean (Peñuelas and Boada 2003; Jump and Peñuelas 2006) and in central European sites NW of our study area (Geßler et al. 2007).
Climatic and phenological data originated from the Environmental Agency of the Republic of Slovenia within the Ministry of the Environment and Spatial Planning. We thank Prof. Dr. Lučka Kajfež-Bogataj for enabling us to use them. We thank Marko Beber, Martin Zupančič and Luka Krže for their work in the field and laboratory. The work was funded by the Ministry of Higher Education, Science and Technology of the Republic of Slovenia, Research Program “Lesarstvo”, and by the Spanish Ministry of Education and Science, project CGL2005-04270.