The formation of wood results from cambial activity and its anatomical properties reflect the variability of environmental conditions during the growing season. Recently, it was found that wood density variations in conifers growing under cold-limited environment result from the adjustment of cell wall thickness (CWT) to temperature. Additionally, it is known that intra-annual density fluctuations (IADFs) are formed in response to precipitation after the summer drought. Although IADFs are frequent in Mediterranean conifers no study has yet been conducted to determine if these structures result from the adjustment of lumen diameter (LD) or CWT to soil water availability. Our main objective is to investigate the intra-ring variation of wood anatomical features (LD and CWT) in Pinus pinaster Ait. growing under a water-limited environment. We compared the tracheidograms of LD and CWT for the years 2010–2013 in P. pinaster growing in the west coast of Portugal. Our results suggest a close association between LD and soil moisture content along the growing season, reinforcing the role of water availability in determining tracheid size. Compared with CWT, LD showed a higher intra- and inter-annual variability suggesting its strong adjustment value to variations in water availability. The formation of a latewood IADF appears to be predisposed by higher rates of cell production in spring and triggered by early autumn precipitation. Our findings reinforce the crucial role of water availability on cambial activity and wood formation in Mediterranean conifers, and emphasize the high plasticity of wood anatomical features under Mediterranean climate.
Citation: Carvalho A, Nabais C, Vieira J, Rossi S, Campelo F (2015) Plastic Response of Tracheids in Pinus pinaster in a Water-Limited Environment: Adjusting Lumen Size instead of Wall Thickness. PLoS ONE 10(8): e0136305. doi:10.1371/journal.pone.0136305
Editor: Eryuan Liang, Chinese Academy of Sciences, CHINA
Received: April 8, 2015; Accepted: August 2, 2015; Published: August 25, 2015
Copyright: © 2015 Carvalho et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited
Data Availability: All relevant data are within the paper and its Supporting Information files.
Funding: This study was supported by the Fundação para a Ciência e a Tecnologia, Ministério da Educação e Ciência (FCT) co-financed by Compete, through the projects PTDC/AAC-AMB/111675/2009 and EXPL/AAG-GLO/1885/2013, and CFE strategic program UI0134-UID/BIA/04004/2013. Filipe Campelo was supported by a postdoctoral research grant (SFRH/BPD/47822/2008) from FCT with funds from POPH (Portuguese Operational Human Potential Program) and QREN Portugal (Portuguese National Strategic Reference Framework).
Competing interests: The authors have declared that no competing interests exist.
Wood is formed by the vascular cambium that is controlled by intrinsic (e.g. plant hormones) and extrinsic factors (e.g. temperature and precipitation). Thus, the variability of climatic conditions during the growing season can affect cambial activity [1, 2] and tree rings properties by changing the number of xylem cells produced and/or their anatomical properties . The intra-ring variation of wood anatomical parameters, such as wood density  and vessel lumen area , is correlated with specific climatic conditions and, therefore, can be used as climatic proxies [6–8]. In fact, several studies have found that chronologies of wood anatomical features can have a better climatic signal than tree-ring width chronologies [5, 9].
Xylem anatomy can thus provide valuable information on the environmental conditions controlling cambial activity and cell growth throughout the growing season [10, 11]. For example, Pinus nigra Arn. and Pinus sylvestris L. from a mesic Mediterranean forest in Spain reduced ring width, tracheid lumen and wall thickness in response to warm and dry summers . Also in Spain, it was observed that tacheid size of Juniperus thurifera L. at the beginning of the growing season was strongly correlated with late winter climatic conditions, with a warmer February leading to the formation of larger tracheids . Additionally, it was found that J. thurifera trees from drier sites presented thicker and smaller tracheids . Adaptations in tracheid anatomy were also observed in a continental site in Switzerland where P. sylvestris from a dry site showed narrower tree rings and lower latewood proportions compared to a mesic site . These studies indicate that cellular parameters respond to environmental conditions at the time of their formation .
Trees are affected by inter- and intra-annual changes in climatic conditions, and the information recorded in xylem is important to understand the effect of climate on wood growth dynamics. Under Mediterranean climate, evergreen trees show two periods of activity, one in spring and another in autumn, associated with mild temperatures and high soil-water availability, and two periods of growth reduction or pause, limited by temperature in winter and water availability in summer [17, 18]. In fact, xylogenesis of conifers under Mediterranean climate showed cambial activity in spring, a reduction or cessation of xylogenesis during summer, followed by cambial resumption in autumn [3, 19, 20]. The autumn resumption of cambial activity is frequently associated with the formation of intra-annual density fluctuations (IADFs), which are visually characterized as earlywood-like cells within latewood .
IADFs are often observed in trees growing under Mediterranean climate [22, 23] and their relative position within tree rings can be used to estimate when the triggering factor occurred . Latewood IADFs have been related to above-average precipitation in autumn [24, 25], whereas earlywood IADFs, characterized as latewood-like cells within earlywood, were observed in years with low precipitation in spring . The incorporation of intra-ring anatomical features in ecological and climatological studies can improve and/or reveal new climatic signals [15, 26] and add new information about the meteorological events that took place during the growing season . Wood growth dynamics of Pinus pinaster Ait. under Mediterranean climate has been previously investigated [2, 27, 28]. Wider tree-rings were formed due to a higher rate of cell division, rather than by a longer period of xylogenesis . The higher rate of cell division was associated with high water availability in spring, as observed by xylogenesis studies  and correlation analysis of tree-ring width and climatic conditions [25, 29]. A study on stem radial variation in P. pinaster also showed a clear response to water availability in the daily and seasonal pattern, with marked stem contractions and re-hydrations observed in summer and autumn, respectively . The formation of latewood IADFs in P. pinaster is associated with water availability after the summer drought [25, 28]. This is supported by the positive correlations found between latewood IADFs frequency and September precipitation [24, 31, 32], and by anatomical observations where the resumption of cambial activity and formation of a latewood IADF was observed . All previous studies point out that water availability plays a major role in cambial activity and wood formation under Mediterranean climate. Our main objective was to investigate the intra-ring variation of wood anatomical characteristics, such as lumen diameter (LD) and cell wall thickness (CWT), in P. pinaster growing under a water-limited environment. To address this, we analyzed the tracheidograms of four consecutive years with different climatic conditions. Tracheidograms represent the variation of a given tracheid feature within a tree ring, and can provide new and additional information on the environmental conditions during the growing season improving our capacity to reconstruct past climate [33, 34]. To this end we compared the intra-ring variation of LD with the intra-seasonal variation of soil water availability.
Material and Methods
Study area and tree selection
The study was carried out in the "Perímetro florestal dunas de Cantanhede" with the permission of the "Instituto da Conservação da Natureza e das Florestas". The study species, Pinus pinaster, is not an endangered or protected species. Perímetro florestal dunas de Cantanhede is a plantation of P. pinaster on sand dunes (40°21’35.15” N, 8°49’10.06” W; 15 m a.s.l.), located in the west coast of Portugal. The study area had a density of approximately 230 trees ha−1 and is characterized by dominant and codominant trees with an average age of 45 years. Ten trees without stem or crown anomalies were randomly selected. The climate is typically Mediterranean with oceanic influence, the summer is dry and the precipitation is more abundant in autumn and winter (Fig 1).
Monthly mean temperature and precipitation data were downloaded from the Royal Netherlands Meteorological Institute (http://climexp.knmi.nl), for the closest grid point (CRU TS 3, 0.5° × 0.5°). For the last 30 years, the mean annual temperature was 16° C and the total annual precipitation was 900 mm. For the period 2010–2013, minimum and maximum daily temperatures and total daily precipitation were obtained from the closest meteorological station located in Figueira da Foz, at 25 km south from the study site.
Sample preparation and measurements
One wood microcore per tree (n = 10) was collected on the south-facing side of the stem in April 2014 using a Trephor . These microcores were placed in eppendorfs with 50% alcohol solution and stored at 5° C to preserve cells from degradation. In the laboratory, the microcores were dehydrated using a graded alcohol series and D-limonene, and embedded in paraffin . Transverse sections 5–7 μm thick were cut from the samples with a rotary microtome, stained with 1% aqueous safranin and permanently mounted on glass slides with Canada balsam (Eukitt). Digital images were taken at 200 x magnification with a digital camera fixed on a microscope (Fig 2).
Images were analyzed using ImageJ (http://rsbweb.nih.gov/ij/). In each ring, three radial paths were selected to measure radial lumen diameter (LD), cell wall thickness (CWT) and the ratio of LD to CWT (LD/CWT) along the tree rings. For each selected radial file, the number of tracheids (nCells) was determined and tracheids were classified in earlywood and latewood following the Mork's formula . When the LD/CWT ratio was ≥ or < 2, tracheids were classified as earlywood (Ew) or latewood (Lw), respectively. Latewood IADFs are characterized by earlywood-like cells within latewood, thus, we considered that an IADF was formed when the LD/CWT ratio was ≥ 2 after the occurrence of the first latewood tracheid. The “width” of the latewood IADF was given by the number of tracheids inside the latewood showing a LD/CWT ratio ≥ 2 (nIADFs).
Tracheidograms represent the intra-ring variation of an anatomical parameter in the radial direction according to its relative position within the ring (S1 Fig; S1 Table) . To allow the comparison of tracheidograms with different number of cells, we normalized the number of cells per tracheidogram to a constant number of cells (S2 Table), using dedicated R functions (based on the tgram package for R ) that computes the relative position of each tracheid considering that all rings have the same number of cells. The normalized tracheidogram was 25 cells (16 for earlywood and 9 for latewood). To describe changes in anatomical features (LD, CWT and LD/CWT) we used Generalized Additive Models (GAMs). In this study, the anatomical feature (e.g. LD) was expressed as a function of the position of the cell: (1) where y is the vector of the anatomical feature (e.g. LD), nCell is the vector of the corresponding standardized cell number, s is an unspecified smooth function, α is the intercept, and ԑ is the error term. GAMs were also used to investigate intra-ring variability of anatomical features: (2) where ROC(y) is the rate of change of the anatomical feature (in percentage) that represents the increase or decrease of the current tracheid relative to the previous tracheid. GAMs were fitted in R using the mgcv package . Changes in the mean of anatomical variables over the four years (2010–2013) were investigated using repeated-measure ANOVA. When the dependent variable (years) was statistically significant in the ANOVA test (p < 0.01), the Bonferroni corrected pair-wise comparisons were computed to identify specific differences between years. Before running the ANOVA, log transformations of the data were applied when necessary to fulfill the requirements of the statistical analysis for normal distribution and homogeneity of variance.
Monthly soil moisture was estimated using a water balance model . Monthly temperature and precipitation (from the nearest CRU grid point) were used as input data and evapotranspiration, surface runoff, and groundwater flow were estimated by the model. Since soil in the study area is sandy with low organic matter content and low water-holding capacity, the model was run considering that the maximum moisture held by the soil was 0.35 v/v (volume per volume). For each year, LD along the tree ring was visually compared with the monthly soil moisture, considering that the growing season started in March and ended in October, with the transition between earlywood and latewood being set to the middle of June. The timings of xylem formation were based on the observations previously gathered from the same species and in the same site [2, 28]. This approach represents a simplification of the cambial activity by considering that the growing season length is constant and the transition from earlywood to latewood occurs in the same period for different years. Therefore, we assume that the cell division rate of earlywood (latewood) only depends on the number of tracheids differentiated into earlywood (latewood) which can vary from year to year.
Climate during 2010–2013
The four studied years presented a lower mean annual temperature than the long-term mean (1984–2013) (Table 1). The average temperature of July and August was higher in 2010 and 2013 than in 2011 and 2012 (Fig 1). Total annual precipitation and the seasonal distribution of precipitation were different between the four years. Contrary to the other years, 2012 had few precipitation events from January to March, while in 2013 precipitation in March was very high (168 mm). In the summer of 2010 and 2013, precipitation was extremely low, while in 2012 it was higher with more than 20 mm in August. Precipitation in September 2012 and 2013 were above the long-term mean. Comparing the four studied years, soil moisture in March and August showed the highest and lowest values in 2013, and in September soil moisture was higher in 2012 (Table 1).
The total number of tracheids (nCells; F(3,27) = 18.57, p < 0.001), earlywood (nEw; F(3,27) = 15.29, p < 0.001), latewood tracheids (nLw; F(3,27) = 15.76, p < 0.001), and IADFs tracheids (nIADFs; F(3,27) = 15.66, p < 0.001) was significantly different between years (Fig 3).
Anatomical variables: number of cells (nCells), number of earlywood tracheids (nEw), number of latewood tracheids (nLw), number of earlywood-like tracheids within the latewood (nIADFs), cell wall thickness of the earlywood (EwCWT) and lumen diameter of latewood (LwLD). Data are the means ± 2SE and different letters indicate significant differences between years.
The mean LD of earlywood was not significantly different between years (F(3,27) = 4.22, p > 0.01). The mean LD of latewood was significantly different between years (F(3,27) = 14.36, p < 0.001), with 2013 showing the highest value (Fig 3). There was a statistically significant difference between years for CWT of earlywood (F(3,27) = 9.63, p < 0.001), with the post-hoc test showing that the mean CWT of earlywood in 2013 was higher than in 2012 and 2011. The mean CWT of latewood was not significantly different between years (F(3,27) = 3.58, p > 0.01). In 2013, LD and CWT of IADF tracheids presented mean (± SE) values of 18.35 (± 1.25) and 6.17 (± 0.30) μm, respectively, whereas true latewood tracheids had lower values of LD (9.05 ± 0.48 μm) and slightly higher for CWT (7.54 ± 0.17 μm).
The standardized tracheidograms of anatomical features showed that the intra- and inter-annual variability of LD was higher when compared to CWT (Fig 4A and 4B and S2 Fig). In general, LD gradually decreased from 30–40 to 5–10 μm (Fig 4A), whereas CWT gradually increased from 3–4 to 7–8 μm, decreasing afterwards to 5–6 μm in the last 5 tracheids (Fig 2B). Although LD of the 5–10 tracheids was slightly lower in 2013 than in the other years (Fig 4A), the mean LD of earlywood was not different between years. On the contrary, CWT of earlywood showed differences between years (Fig 3). This is reflected in the lower values of the LD/CWT ratio of the earlywood tracheids of 2013 (Fig 4C). In 2012 and 2013 the decreasing trend of LD was inverted after the beginning of latewood, with the LD of the 22–24 cells in 2013 being higher than in the other years (Fig 2A). Indeed, a clear latewood IADF was produced in 2013, with earlywood-like cells within latewood and a LD/CWT ratio ≥ 2 (Fig 4C and S2 Table). LD can show one or two peaks, one in earlywood and another in latewood, whereas CWT only shows a single peak in the transition between earlywood and latewood.
The number of tracheids per ring was set to 25 and each standardize tracheidogram contains 16 tracheids in earlywood (Ew) and 9 in latewood (Lw). A) Lumen diameter (LD); B) Cell wall thickness (CWT); C) Ratio of LD to CWT (LD/CWT). The color lines represent the means and the shaded areas the 95% confidence intervals.
Synchronization of LD and soil moisture
The seasonal variation in soil moisture is related to the precipitation pattern, with higher moisture in winter and autumn (0.30–0.35 v/v) and lower values in summer (0.05–0.10 v/v) (Fig 5). In summer 2010 and 2013, soil moisture showed the lowest values (< 0.10 v/v) associated with high summer temperatures (Fig 1). In September 2013, soil moisture recovered after the rain events, while in 2010 low soil moisture persisted until the end of September (Fig 5). Analyzing the pattern of soil moisture and LD of tracheids, there is a close association between both variables along the growing season, with the decrease in soil moisture from March to June closely accompanied by a decrease in LD. The increase in soil moisture after the summer drought in 2012 and 2013 was followed by a clear increase in LD only in 2013 (Fig 5).
In this study, we investigated the anatomical features of tracheids in P. pinaster and its coordination with the climatic conditions over four years in a water-limited environment. The main anatomical differences observed among the four years were a higher number of tracheids in 2013, compared to 2010–2012, and the formation of latewood IADFs in 2012 and 2013, although more evident in 2013. In 2013, LD was 2 times larger for IADF tracheids than for true latewood, whereas the CWT was only 0.2 times thicker for true latewood than for IADF tracheids.
Under Mediterranean climate, cambial activity is mainly controlled by water availability during the growing season [10, 22]. In 2013 the high availability of water at the start of the growing season probably allowed the formation of more tracheids, resulting in a wider tree-ring. Indeed, previous studies found that water availability during spring was related to an increase in the rate of cell production in P. pinaster . Similarly, the earlywood width in P. halepensis and P. pinea was strongly correlated with spring precipitation [21, 39]. Additionally, variations in water availability throughout the growing season can affect the anatomical features of tracheids . Tracheid size represents an important trade-off between hydraulic conductivity and vulnerability to cavitation [40–42], and is highly related to water availability during the cell enlargement phase [13, 14, 24]. In the enlargement phase the pressure potential of the apoplastic water is essential for cell expansion, since it has to be higher than the symplastic water potential for water to enter the expanding cell . This is reinforced by the close association between LD and soil moisture content, with the transition from early- to latewood associated with a decrease in water availability. Our results suggest that the earlywood-latewood transition occurs when soil moisture is <0.15 v/v, which is in agreement with previous studies showing that drier conditions trigger the start of latewood formation .
The average earlywood LD was similar among the four studied years. However, when comparing the standardize tracheidograms, between the 5th and 10th tracheid the LD was lower in 2013 compared with the other years. It seems that in 2013, although a higher number of tracheids was produced due to better moisture conditions in the beginning of the growing season, the LD was smaller and CWT larger. This supports the findings of Cuny and co-authors , which observed that tracheid diameter is strongly affected by the rate of cell production, with higher rates of cell division associated with narrower tracheids. It is known that auxin plays an important role in the enlargement phase . The concentration of auxin presents a maximum in the cambial zone decreasing towards the differentiating xylem where it reaches a low and stable value close to the transition between enlargement and cell-wall thickening cells . The width of this gradient determines the width of the enlargement zone and determines the time cells spend in that phase . Under higher rates of cell division, the newly divided cells push the previous cells out of the enlargement zone, towards the cell wall thickening zone, decreasing the time spent by cells in enlargement, and consequently reducing LD. This suggests that LD is not only determined by soil water availability but also by the amount of time cells spend in the enlargement zone, which in turn depends on the rate of cell production.
Our results showed a higher inter-annual variability of LD, compared to CWT, suggesting that wood anatomical variations among different years were mainly caused by changes in LD, with an apparent coordination with soil-water availability along the growing season. Contrasting results were found by Fonti and co-authors , who reported that in trees of Larix sibirica Ldb. growing in southern Siberia, the adjustment of xylem was mainly reflected in changes of CWT and highly dependent on temperature. The differences observed in the response of trees growing under water- and temperature-limited environments reflect the dominant environmental constraints to cambial activity. In cold-limited environments trees have to guarantee that lignification ends before the start of winter [48, 49]. Therefore, the adjustment of tracheid features in cold environments occurs in the lignification phase and not in the enlargement phase, as observed in water-limited environments. Nonetheless, Cuny and co-authors  showed that changes in CWT are driven by cell size, with the amount of material deposited per cell being almost constant along most of the tree ring. Thus, the increase in CWT in latewood cells is the result of a similar amount of lignin placed in a smaller lumen volume. This relation is noticeably seen in our results when comparing the opposite patterns of the tracheidograms of LD and CWT.
The formation of a latewood IADF was clearly observed in 2013 and marginally in 2012. Previous studies showed a strong correlation between latewood IADFs and September precipitation [24, 25, 29, 31, 50]. The release of water stress after the summer drought can induce the resumption of cambial activity and consequent entrance of the new cells into the enlargement zone. The recovery of the tree water status  permits cells to expand more than true latewood cells. As a result, in 2013 a clear latewood IADF was formed, with 11 out of 27 latewood cells to be considered as earlywood-like cells (LD/CWT ≥ 2). This finding suggests that the combination of a dry summer and wet early autumn is necessary to trigger the formation of a latewood IADF [2, 24]. This is reinforced by the fact that in 2010 and 2011, with low precipitation events in September, no latewood IADF was formed. In 2012, although there were rainfall events in September, only a marginal latewood IADF was formed, suggesting that other factors are also involved in IADF formation . Previous studies showed that wider tree rings are more prone to form IADFs than smaller rings . We believe that the formation of a latewood IADF in 2013 was predisposed by the higher rates of cell production and triggered by the rainfall events after the summer drought. The higher soil water availability during the start of the growing season induces higher rates of cell production which, in turn, increases the number of cells under enlargement after the summer drought, predisposing the formation of an IADF in response to September precipitation.
Pinus pinaster trees show a high capacity to adjust the size of their tracheids to the current soil water content. Conifers growing under water-limited environments appear to adjust LD, while in temperature-limited environments conifers adjust CWT  We hypothesized that the formation of latewood IADFs is predisposed by high rates of cell production and triggered by the combination of a dry summer followed by a wet early autumn. However, our observations are only based in 4 years, limiting our conclusions. Further experimental studies are thus necessary to understand (i) if soil moisture content along the growing season is the major driving force of LD; (ii) if higher moisture content in the beginning of the growing season actually leads to a higher rate of cell production; and (iii) if the formation of latewood IADFs is predisposed by higher rates of cell production and triggered by precipitation events after the summer drought.
S1 Fig. Tracheidograms for the period 2010–2013, the number of tracheids corresponds to the mean number of cells.
A) Lumen diameter (LD); B) Cell wall thickness (CWT); C) Ratio of LD to CWT (LD/CWT). The color lines represent the means, the shaded areas the 95% confidence intervals and filled dots represent latewood tracheids.
S2 Fig. Rate of variation (in percentage) of standardized tracheidograms, for the period 2010–2013.
The number of tracheids per ring was set to 25 and each standardize tracheidogram contains 16 tracheids in earlywood (Ew) and 9 in latewood (Lw). A) Lumen diameter (LD); B) Variation of cell wall thickness (CWT); C) Ratio of LD to CWT (LD/CWT). The color lines represent the means, the shaded areas the 95% confidence intervals.
Mean ± SE of lumen diameter (LD), cell wall thickness (CWT) and ratio of LD to CWT (LD/CWT) in function of cell position for the period 2010–2013.
This study profited from discussions and activities within the framework of the COST Action STReESS (COST FP1106). The authors would like to thank two anonymous reviewers for helpful comments and suggestions on an earlier version of the manuscript.
Conceived and designed the experiments: FC. Performed the experiments: AC JV FC. Analyzed the data: FC SR. Contributed reagents/materials/analysis tools: FC. Wrote the paper: AC CN JV SR FC. Designed the software used in analysis: FC.
- 1. Boulouf Lugo J, Deslauriers A, Rossi S (2012) Duration of xylogenesis in black spruce lengthened between 1950 and 2010. Ann Bot 110:1099–1108. doi: 10.1093/aob/mcs175. pmid:23041380
- 2. Vieira J, Rossi S, Campelo F, Freitas H, Nabais C (2014) Xylogenesis of Pinus pinaster under a Mediterranean climate. Ann For Sci 71:71–80. doi: 10.1007/s13595-013-0341-5.
- 3. Camarero JJ, Olano JM, Parras A (2010) Plastic bimodal xylogenesis in conifers from continental Mediterranean climates. New Phytol 185:471–80. doi: 10.1111/j.1469-8137.2009.03073.x. pmid:19895415
- 4. Franceschini T, Longuetaud F, Bontemps J-D, Bouriaud O, Caritey B-D, Leban J-M (2013) Effect of ring width, cambial age, and climatic variables on the within-ring wood density profile of Norway spruce Picea abies (L.) Karst. Trees 27:913–925. doi: 10.1007/s00468-013-0844-6.
- 5. Campelo F, Nabais C, Gutiérrez E, Freitas H, García-González I (2010) Vessel features of Quercus ilex L. growing under Mediterranean climate have a better climatic signal than tree-ring width. Trees 24:463–470. doi: 10.1007/s00468-010-0414-0.
- 6. Kirdyanov AV, Vaganov EA, Hughes MK (2006) Separating the climatic signal from tree-ring width and maximum latewood density records. Trees 21:37–44. doi: 10.1007/s00468-006-0094-y.
- 7. Liang E, Eckstein D (2006) Light rings in Chinese pine (Pinus tabulaeformis) in semiarid areas of north China and their palaeo-climatological potential. New Phytol 171:783–791. doi: 10.1111/j.1469-8137.2006.01775.x. pmid:16918549
- 8. Fonti P, von Arx G, García-González I, Eilmann B, Sass-Klaassen U, Gärtner H et al. (2010) Studying global change through investigation of the plastic responses of xylem anatomy in tree rings. New Phytol 185:42–53. doi: 10.1111/j.1469-8137.2009.03030.x. pmid:19780986
- 9. Novak K, de Luís M, Raventós J, Čufar K (2013) Climatic signals in tree-ring widths and wood structure of Pinus halepensis in contrasted environmental conditions. Trees 27:927–936. doi: 10.1007/s00468-013-0845-5.
- 10. Zweifel R, Zimmermann L, Zeugin F, Newbery DM (2006) Intra-annual radial growth and water relations of trees: implications towards a growth mechanism. J Exp Bot 57:1445–59. doi: 10.1093/jxb/erj125. pmid:16556628
- 11. Abrantes J, Campelo F, García-González I, Nabais C (2013) Environmental control of vessel traits in Quercus ilex under Mediterranean climate: relating xylem anatomy to function. Trees 27:655–662. doi: 10.1007/s00468-012-0820-6.
- 12. Martin-Benito D, Beeckman H, Cañellas I (2012) Influence of drought on tree rings and tracheid features of Pinus nigra and Pinus sylvestris in a mesic Mediterranean forest. Eur J For Res 132:33–45. doi: 10.1007/s10342-012-0652-3.
- 13. Olano JM, Eugenio M, García-Cervigón AI, Folch M, Rozas V (2012) Quantitative tracheid anatomy reveals a complex environmental control of wood structure in continental Mediterranean climate. Int J Plant Sci 173:137–149. doi: 10.1086/663165.
- 14. DeSoto L, Cruz MD la, Fonti P (2011) Intra-annual patterns of tracheid size in the Mediterranean tree Juniperus thurifera as an indicator of seasonal water stress. Can J For Res 41:1280–1294. doi: 10.1139/X11-045.
- 15. Rigling A, Bräker O, Schneiter G, Schweingruber F (2002) Intra-annual tree-ring parameters indicating differences in drought stress of Pinus sylvestris forests within the Erico-Pinion in the Valais (Switzerland). Plant Ecol 163:105–122.
- 16. Deslauriers A, Morin H (2004) Intra-annual tracheid production in balsam fir stems and the effect of meteorological variables. Trees 19:402–408. doi: 10.1007/s00468-004-0398-8.
- 17. Mitrakos K (1980) A theory for Mediterranean plant life. Acta Oecologica 1:245–252.
- 18. Gutiérrez E, Campelo F, Camarero JJ, Ribas M, Muntán E, Nabais C et al. (2011) Climate controls act at different scales on the seasonal pattern of Quercus ilex L. stem radial increments in NE Spain. Trees 25:637–646. doi: 10.1007/s00468-011-0540-3.
- 19. Linares JC, Camarero JJ, Carreira JA (2009) Plastic responses of Abies pinsapo xylogenesis to drought and competition. Tree Physiol 29:1525–36. doi: 10.1093/treephys/tpp084. pmid:19801556
- 20. de Luis M, Novak K, Raventós J, Gričar J, Prislan P, Čufar K (2011) Cambial activity, wood formation and sapling survival of Pinus halepensis exposed to different irrigation regimes. For Ecol Manage 262:1630–1638. doi: 10.1016/j.foreco.2011.07.013.
- 21. Campelo F, Nabais C, Freitas H, Gutiérrez E (2007) Climatic significance of tree-ring width and intra-annual density fluctuations in Pinus pinea from a dry Mediterranean area in Portugal. Ann For Sci 64:229–238. doi: 10.1051/forest.
- 22. Cherubini P, Gartner BL, Tognetti R, Bräker OU, Schoch W, Innes JL (2003) Identification, measurement and interpretation of tree rings in woody species from mediterranean climates. Biol Rev Camb Philos Soc 78:119–148. pmid:12620063
- 23. Rozas V, García-González I, Zas R (2011) Climatic control of intra-annual wood density fluctuations of Pinus pinaster in NW Spain. Trees 25:443–453. doi: 10.1007/s00468-010-0519-5.
- 24. Vieira J, Campelo F, Nabais C (2009) Age-dependent responses of tree-ring growth and intra-annual density fluctuations of Pinus pinaster to Mediterranean climate. Trees 23:257–265. doi: 10.1007/s00468-008-0273-0.
- 25. Campelo F, Vieira J, Nabais C (2013) Tree-ring growth and intra-annual density fluctuations of Pinus pinaster responses to climate: does size matter? Trees 27:763–772. doi: 10.1007/s00468-012-0831-3.
- 26. Tessier L, Guibal F, Schweingruber FH (1997) Research strategies in dendroecology and dendroclimatology in mountain environments. Clim Change 36:499–517.
- 27. Vieira J, Rossi S, Campelo F, Nabais C (2013) Are neighboring trees in tune? Wood formation in Pinus pinaster. Eur J For Res 133:41–50. doi: 10.1007/s10342-013-0734-x.
- 28. Vieira J, Campelo F, Rossi S, Carvalho A, Freitas H, Nabais C (2015) Adjustment capacity of maritime pine cambial activity in drought-prone environments. PLoS One 10:e0126223. doi: 10.1371/journal.pone.0126223. pmid:25961843
- 29. Nabais C, Campelo F, Vieira J, Cherubini P (2014) Climatic signals of tree-ring width and intra-annual density fluctuations in Pinus pinaster and Pinus pinea along a latitudinal gradient in Portugal. Forestry 87:598–605. doi: 10.1093/forestry/cpu021.
- 30. Vieira J, Rossi S, Campelo F, Freitas H, Nabais C (2013) Seasonal and daily cycles of stem radial variation of Pinus pinaster in a drought-prone environment. Agric For Meteorol 180:173–181. doi: 10.1016/j.agrformet.2013.06.009.
- 31. Campelo F, Vieira J, Battipaglia G, de Luis M, Nabais C, Freitas H et al. (2015) Which matters most for the formation of intra-annual density fluctuations in Pinus pinaster: age or size? Trees 29:237–245. doi: 10.1007/s00468-014-1108-9.
- 32. de Luis M, Novak K, Raventós J, Gričar J, Prislan P, Čufar K (2011) Climate factors promoting intra-annual density fluctuations in Aleppo pine (Pinus halepensis) from semiarid sites. Dendrochronologia 29:163–169. doi: 10.1016/j.dendro.2011.01.005.
- 33. Vaganov EA (1990) The tracheidogram method in tree-ring analysis and its application. In: Cook E, Kairiukstis L (eds) Methods Dendrochronology Appl. Environ. Sci. Kluwer Academic Publishers, Dordrecht, Netherlands, pp 63–116
- 34. Fonti P, Bryukhanova MV, Myglan VS, Kirdyanov AV, Naumova OV, Vaganov EA (2013) Temperature-induced responses of xylem structure of Larix sibirica (Pinaceae) from Russian Altay. Am J Bot 100:1–12. doi: 10.3732/ajb.1200484. pmid:23660567
- 35. Rossi S, Anfodillo T, Menardi R (2006) Trephor: A new tool for sampling microcores from tree stems. Iawa J 27:89–97. doi: 10.1163/22941932-90000139.
- 36. Denne M (1988) Definition of latewood according to Mork. Iawa Bull 10:59–62.
- 37. Wood SS (2006) Generalized additive models: An introduction with R. doi: 10.1111/j.1541-0420.2006.00574.x.
- 38. Huang J, van den Dool HM, Georgakakos K (1996) Analysis of model-calculated soil moisture over the United States (1931–1993) and applications to long-range temperature forecasts. J Clim 9:1350–1362.
- 39. Pasho E, Julio Camarero J, Vicente-Serrano SM (2012) Climatic impacts and drought control of radial growth and seasonal wood formation in Pinus halepensis. Trees 26:1875–1886. doi: 10.1007/s00468-012-0756-x.
- 40. Hacke UG, Sperry JS (2001) Functional and ecological xylem anatomy. Perspect Plant Ecol Evol Syst 4:97–115. doi: 10.1078/1433-8319-00017.
- 41. Domec J-C, Gartner BL (2002) How do water transport and water storage differ in coniferous earlywood and latewood? J Exp Bot 53:2369–2379. doi: 10.1093/jxb/erf100. pmid:12432029
- 42. Willson CJ, Jackson RB (2006) Xylem cavitation caused by drought and freezing stress in four co-occurring Juniperus species. Physiol Plant 127:374–382. doi: 10.1111/j.1399-3054.2006.00644.x.
- 43. Abe H, Nakai T, Utsumi Y, Kagawa A (2003) Temporal water deficit and wood formation in Cryptomeria japonica. Tree Physiol 23:859–63. pmid:12865252
- 44. Cuny HE, Rathgeber CBK, Frank D, Fonti P, Fournier M (2014) Kinetics of tracheid development explain conifer tree-ring structure. New Phytol 203:1231–1241. doi: 10.1111/nph.12871. pmid:24890661
- 45. Perrot-Rechenmann C (2010) Cellular responses to auxin: division versus expansion. Cold Spring Harb Perspect Biol 2:a001446. doi: 10.1101/cshperspect.a001446. pmid:20452959
- 46. Sundberg B, Uggla C, Tuominen H (2000) Cambial growth and auxin gradients. In: Savidge R, Barnett J, Napier R (eds) Cell Mol. Biol. wood Form. Oxford, UK: BIOS Scientific Publishers Ltd, pp 169–188
- 47. Uggla C, Moritz T, Sandberg G, Sundberg B (1996) Auxin as a positional signal in pattern formation in plants. Proc Natl Acad Sci U S A 93:9282–9286. doi: 10.1073/pnas.93.17.9282. pmid:11607701
- 48. Rossi S, Deslauriers A, Gričar J, Seo J-W, Rathgeber CBK, Anfodillo T et al. (2008) Critical temperatures for xylogenesis in conifers of cold climates. Glob Ecol Biogeogr 17:696–707. doi: 10.1111/j.1466-8238.2008.00417.x.
- 49. Gričar J, Čufar K, Oven P, Schmitt U (2005) Differentiation of terminal latewood tracheids in silver fir trees during autumn. Ann Bot 95:959–65. doi: 10.1093/aob/mci112. pmid:15760912
- 50. Vieira J, Campelo F, Nabais C (2010) Intra-annual density fluctuations of Pinus pinaster are a record of climatic changes in the western Mediterranean region. Can J For Res 40:1567–1575. doi: 10.1139/X10-096.