Functional Ecology 2005 19, 941–951 Growth, demography and carbon relations of Polylepis trees at the world’s highest treeline Blackwell Publishing, Ltd. G. HOCH† and C. KÖRNER Institute of Botany, University of Basel, Schönbeinstrasse 6, CH-4056 Basel, Switzerland Summary 1. Growth, reproductive success and non-structural carbon pools in Polylepis tarapacana Philippi trees were examined across a transect between 4360 and 4810 m altitude on Nevado Sajama, Bolivia. 2. The mean −10-cm soil temperature of 5·4 °C under trees at the treeline during the 265-day growing season matched the threshold temperature found at other subtropical and tropical treelines. Beyond 4400 m Polylepis is restricted to the warmer and drier equator-facing slopes, suggesting a direct thermal limitation of tree growth. 3. Maximum tree height, annual shoot increment and mean tree-ring width decreased with altitude. Trees near the upper range limit reached a maximum tree height of 3·3 m and a maximum stem diameter of 34 cm. 4. The smallest tree-height classes dominated populations at all altitudes, and the uppermost site revealed the highest proportion of seedlings. Tree-size demography indicates a critical phase for tree establishment during the sapling stage, when trees emerge from sheltered niches near the ground. 5. No evidence of a depletion of mobile C stores (sugars, starch and lipids) was found in any tissue type with increasing elevation, suggesting a limitation of C investment (growth) rather than C acquisition (photosynthesis) at treeline. Key-words: Andes, carbohydrates, forest limit, high elevation, temperature Functional Ecology (2005) 19, 941–951 doi: 10.1111/j.1365-2435.2005.01040.x Introduction Although high-altitude treelines are a worldwide phenomenon, ecophysiological studies at high elevations have mainly been conducted in the past at midand high-latitude mountain ranges. Thus numerous attempts at a functional explanation of treeline formation concern mechanisms tied to high-latitude climatic conditions, especially the presence of a long, cold and snow-rich winter season (for a summary of hypotheses see Tranquillini 1979; Wardle 1993; Körner 1998; Holtmeier 2003). For a unifying, globally valid theory of treeline formation, data from tropical and subtropical regions are therefore needed. Trees at low-latitude treelines experience climatic conditions that differ substantially from those at higher latitudes. Diurnal air temperature amplitudes at low latitudes are often more pronounced than those between seasons (Larcher 1975; Hardy et al. 1998), and the duration of the growing season is markedly longer than the duration of the dormant period (with a maximum 365-day growing season at some equato© 2005 British Ecological Society †Author to whom correspondence should be addressed. E-mail: [email protected] rial treelines; Körner & Paulsen 2004). Despite these differences, the mean growing-season temperatures of the vast majority of natural high-altitude treelines are within the range 5·0–7·5 °C, with a global mean of 6·7 ± 0·8 °C (−10-cm soil temperatures; Körner & Paulsen 2004). This suggests that annual minimum and maximum temperatures, as well as the duration of the growing season, are less decisive for the altitudinal position of treelines than are average temperatures during the period of active growth. Other climatic and also edaphic determinants are of more regional significance and are not really relevant on a global scale (Körner 1998). Low rainfall and drought, for instance, are not generally related to altitude and may limit tree growth anywhere. However, it is remarkable that trees reach their highest elevations globally in dry regions such as in Tibet (Miehe et al. 2003) and especially in the South American Andes (Braun 1997). Given that the tree limit is often found close to vital upper montane forests, moisture is unlikely to be responsible for an abrupt tree limit at similar altitudes across larger areas of otherwise varied topography. In the current study, we examined different parameters related to tree growth (including the non-structural carbon pools) in Polylepis tarapacana Philippi (Rosaceae: 941 942 G. Hoch & C. Körner Sanguisorbeae) trees along an altitudinal transect at the volcano Sajama, Bolivia. Additionally, we recorded the first complete annual temperature course for this treeline. Polylepis is a widespread evergreen genus of the equatorial Andes, which includes about 20 species, forming thickets and woodland commonly above 3500 m a.s.l. (Kessler 1995). It appears to be a poor competitor, and with its inherent slow growth it loses terrain to more vigorous species when the environment becomes warmer or more humid. The highest-reaching of all Polylepis species, P. tarapacana has a relatively narrow geographical distribution, reaching from the volcanic western Andean Cordillera in southern Peru to the region of Potosi, southern Bolivia and to adjacent Chile, and its distribution is restricted to volcanic slopes between 3900 and 5100 m a.s.l. (Kessler 1995). The high-altitude P. tarapacana forest belt, which embraces the slopes of the volcano Nevado Sajama, is of special interest for ecophysiological investigations as it constitutes the world’s highest occurrence of truly arborescent plant individuals. The remarkably similar mean growing-season temperatures of ≈6·7 °C at climatic treelines across the globe indicate that temperature-driven mechanisms dominate the formation of high-elevation treelines worldwide. Following from previous studies, the low temperatures at treeline probably first restrict growth processes (meristem activities), while C acquisition continues at more than sufficient rates (Grace, Berninger & Nagy 2002). This hypothesis of a sink limitation of tree growth at climatic treelines (Körner 1998) has gained support from recent surveys which reveal ample provision of treeline trees with C-storage compounds (Hoch & Körner 2003; Shi, Körner & Hoch, 2005), not congruent with a photosynthetic bottleneck of tree growth in cold environments. Here we explore the likelihood of C limitation for tree growth at an altitude where the partial pressure of CO2 is nearly half that at sea level. Materials and methods © 2005 British Ecological Society, Functional Ecology, 19, 941–951 We studied high-altitude populations of Polylepis tarapacana trees at the western front of Nevado Sajama (summit 6542 m a.s.l.) in Oruro province, Bolivia (18°07′ S, 68°57′ W; Fig. 1). The climate is subtropicalalpine with a wet, warm season during the southern hemisphere summer from November to April and a dry, cold season between May and October. Annual precipitation, which is very variable among years (Hardy et al. 1998), averages at ≈330 mm [316 mm at 4220 m a.s.l., 1975 – 85 mean, cited by Hardy et al. (1998) and 347 mm at 4300 m a.s.l., 4-year mean, recorded by M. LibermanCruz cited by Braun (1997)]. On Nevado Sajama, P. tarapacana forms open forest stands between 4200 and 4810 m a.s.l. (with the treeline, defined here as the altitude above which trees Fig. 1. The Polylepis treeline ecotone at Nevado Sajama. (a) Volcano Sajama (6542 m a.s.l.) with the Polylepis tarapacana forest belt between 4200 and 5000 m. White arrows indicate three sampling sites along the transect (see text). (b) Highestgrowing ‘tree-like’ P. tarapacana individuals at 4810 m a.s.l. Trees to the left are ≈3 m high. (c) Overview of the highest sampling site at 4810 m a.s.l. The area studied is marked by the white trapezoid. White cross (×) indicates location of temperature loggers. Note the persons at the corners of the marked plot as a size reference. higher than 3 m are absent; Körner 2003). Shrub-sized individuals of P. tarapacana are found at even higher elevations up to 5100 m a.s.l. (Braun 1997 and references therein), similarly to reports from northern Chile (Troll 1973). Especially at the upper end of the forest belt, P. tarapacana is absent from south-facing (polefacing) slopes, and highest stand densities are found on north- (equator-) to north-east-facing slopes (Braun 1997; Fig. 1a). Irrespective of altitude, P. tarapacana 943 Polylepis at the world’s highest treeline Table 1. Site characteristics of the three investigated Polylepis tarapacana stands at Nevado Sajama Altitude (m a.s.l.) Aspect Inclination (°) Stand density* (trees ha−1) Basal area* (m2 ha−1) 4360 4550 4810 NNW N N 30 30 25 1800 2400 1600 2·1 2·3 1·4 *Estimated across all tree-size classes >5 cm. tends to grow polycormic and forms open ‘dwarf’ forests with tree height rarely exceeding 5 m, although some monocormic individuals at lower altitudes reach maximum heights of ≈7 m. Co-dominant plant species are tussock grasses (Festuca orthophylla, Calamagrostis curvula, Calamagrostis orbignyana); shrubs (Baccharis incarum, Parastrephia lepidophylla, Parastrephia quadrangularis); and cushion plants (Azorella compacta, Pycnophyllum molle). Independent of exposure and inclination, the vegetation cover is low and >50% of the ground is bare soil of volcanic origin. Even at the end of the dry season, we found moist soil at ≈30 cm depth under a layer of dry, insulating volcanic dust, a common feature at high altitudes in regions with low rainfall (Körner 2003). © 2005 British Ecological Society, Functional Ecology, 19, 941–951 Soil temperatures at the treeline were continuously recorded at hourly intervals for a full year from 25 August 2003 – 1 September 2004 by using completely sealed, single-channel thermo-loggers (−5 to +50 °C, Tidbit, Onset, Cape Cod, MA, USA). Following the protocol of Körner & Paulsen (2004), two loggers were buried at −10 cm soil depth beneath P. tarapacana trees under full canopy shade at two sites, one at 4780 m a.s.l. and the other at 4810 m a.s.l. (Fig. 1). As both loggers revealed similar recordings, only mean temperatures for both sites are presented. The temperature loggers were calibrated at the beginning and end of the measurement period in an ice–water mix (0 °C reference point). As in the analyses by Körner & Paulsen (2004), the beginning of the growing season was defined as the date at which the daily mean soil temperatures at −10 cm exceeded 3·2 °C, and the end of the growing season as the date when daily mean soil temperatures dropped below 3·2 °C. Short excursions below 3·2 °C during the warm-rainy season were not excluded. For physical reasons, the 3·2 °C daily mean soil temperatures in shade at 10 cm depth approximate a daily mean air temperature of 0 °C (Körner & Paulsen 2004). We also mounted one sensor in the canopy of a tall tree at 4810 m a.s.l. 2 m above-ground. The sensor was placed on the poleward facing side of the stem under a thick canopy of branches to screen it fully from sky radiation. This shaded sensor recorded a canopy air temperature, which is co-affected by the tree’s aerodynamic properties and solar canopy heating. On 25 August 2003 soil temperature profiles were measured manually in open and tree-covered places on a north- and south-facing slope, at 4550 m a.s.l., using a 3 mm steel probe with a thermistor (Testoterm 110, Testoterm, Lenzkirch, Germany). Here temperatures are presented in °C and temperature differences in K, to avoid confusion between them, as is the custom in bioclimatology and applied physics. Polylepis tarapacana trees were studied at three elevations along an altitudinal transect covering 450 m of altitude from 4360 to 4810 m a.s.l. (Table 1; Fig. 1). At each site the number of tree individuals (excluding seedlings <5 cm) was counted for a randomly chosen area of 10 × 10 m at the lower and middle altitude, and of 30 × 15 m at the uppermost site (Fig. 1), to calculate stand density per hectare. Tree height and maximum stem diameter (disregarding the loose outer bark), as well as the annual length increment of leading branches, were measured for 15 trees per elevation. At each altitude, two stem cores were taken from eight individual trees (>2 m high) using a 5 mm stem corer (Suunto, Finland). Of each stem sampled, one core was kept intact for later tree-ring analyses, while the other was immediately separated into 1·5 cm segments, from the outermost tree ring towards the pith, for chemical analyses. Analyses for starch and sugars revealed strong decreasing concentrations of both compounds from the outermost stem section towards the pith (where concentrations were almost zero), clearly characterizing P. tarapacana as a heartwood-forming species (data not shown). For the current study, only the results for the outermost (youngest) 1·5 cm segments are presented, and are referred to as sapwood. Finally, 5-year-old branchlets were collected from the upper, well lit crown regions of 10 trees (>2 m) at each site, and all leaves and the xylem (with bark and phloem removed with a knife) were sampled separately for chemical analyses. All tissues were sampled on two consecutive days (24 and 25 August 2003) between 11.00 and 14.00 h, and dried at 70–80 °C within a maximum 6 h from sampling. After returning to the Basel laboratory, the intact stem cores were smooth-cut with a razor blade and tree-ring width (±0·01 mm) was measured using an electronic analysis bench (LINTAB, TSAP, Heidelberg, Germany). Because of the irregular growth of Polylepis stems and the frequent occurrence of intermittent 944 G. Hoch & C. Körner layers of damaged tissue (perhaps from fire or fungal infections), we found it impossible to synchronize cores from those trees accurately. We therefore refrained from analysing chronosequences of tree rings, but still estimated the tree age and calculated mean ring widths for each core. Stem cores were also used for the gravimetric determination of sapwood density (mg cm−3). For calculation of specific leaf area (SLA; cm2 g−1) and leaf density (mg cm−3), 10 leaflets were randomly chosen from each sampled branch and dry weight, as well as leaf thickness, determined using a handheld micrometer (±0·01 mm, Teclock Corp., Nagano, Japan). Finally, those leaves were rehydrated in distilled water for 6 h before measuring the leaf area on a photoplanimeter (LI-3050A, Li-Cor, Lincoln, NB, USA). All tissue samples for chemical analyses were re-dried at 75 °C until weight constancy, ground to fine powder, and stored over silica gel at 4 °C until analyses. Parts of the leaf powder were also used for mass spectrometric stable-isotope analysis, in order to assess the systemic water status of the trees. Non-structural carbohydrates Non-structural carbohydrates (NSC) were analysed after Wong (1990), as described in more detail by Hoch & Körner (2003). Non-structural carbohydrates are defined here as the sum of the three most important low molecular-weight sugars (sucrose, glucose and fructose) plus starch. The low molecular-weight sugars were determined photometrically after enzymatic conversions with invertase and phosphoglucose-isomerase. Following an enzymatic degradation of starch to free glucose by a crude fungal amylase (‘Clarase’ from Aspergillus oryzae, Enzyme Solutions Pty Ltd, Crydon South, Victoria, Australia), the sum of free sugars plus starch (NSC) was determined in a separate analysis. The concentration of starch was calculated as NSC minus the free sugars. © 2005 British Ecological Society, Functional Ecology, 19, 941–951 Gas chromatography Gas-chromatography was applied to estimate the contribution of all low molecular-weight carbohydrates (and sugar alcohols) other than those covered by the NSC method. The samples were extracted in methanol : chloroform : water (12 : 5 : 3) at 60 °C for 30 min. After phase separation by addition of water and chloroform, aliquots of the aqueous phases were vacuum dried, silylized with bis(trimethylsilyl)-trifluoroacetamide (BSTFA) and trimethylchlorosilane (TMCS) and analysed on a capillary column (HP1, 30 m × 0·20 mm i.d., 0·2 µm film thickness) on a HP 8690 gas chromatograph (Agilent, CA, USA; detector: FID; analysis software: HP ). Phenyl-β-glucopyranosid was used as internal standard. Nitrogen Total N concentrations were determined in dried samples with a CHN elemental analyser (Vario EL III, Elementar Analysesyteme, Hanau, Germany). Compound concentrations are given on a dry matter (% DM) as well as on a volume (mg cm−3) basis, as higher tissue densities ‘dilute’ non-structural cell compounds on a dry matter basis by a higher proportion of structural compounds. Results for NSC were logtransformed to meet the requirements of normal distribution prior to analyses. All other values were a priori normally distributed and so were computed untransformed. Influence of elevation was analysed by Type III with altitude as fixed factor. A Tukey–Kramer Honest Significant Difference (HSD) test was used to test for significant differences between altitudes. All statistical tests were performed with 3·2·2 (SAS institute, Cary, NC, USA). Results Lipids Lipids (acylglycerols) were determined following the method of Eggstein & Kuhlmann (1974) as described in detail by Hoch & Körner (2003). Following saponification of lipids by extraction of ≈10 mg plant powder in aqueous NaOH for 30 min, the amount of liberated glycerol was determined after enzymatic conversion of glycerol to glycerol-3-phosphate in a 96-well microplate reader. To enable direct comparison of the quantitative contribution of lipids to the whole mobile C pool, we assumed that almost the entire acylglycerols in wood are triacylglycerols, and converted the measured glycerol concentrations to percentage lipids per dry biomass, using a mean triacylglycerol molecular weight of 875 (conservatively assuming the proportion of C17 : C18 fatty acids to be 1 : 1). The −10 cm soil temperature at treeline (mean for 4780 and 4810 m a.s.l.) exhibited a clear seasonality, with warmer temperatures from October to April and cooler temperatures from May to September. The midsummer reduction of temperature (2·5 months) is typically associated with clouds and rain, and we presume that most of the growth of P. tarapacana occurs after this period in March and April. By our purely meteorological definition (see Materials and methods), the growing season lasted for 265 days in 2003/04 (from 29 August 2003 to 21 May 2004; Fig. 2). The mean −10 cm soil temperature during this 265-day period was 5·4 ± 0·1 °C. The minimum and maximum daily means during that period were 2·2 °C (13 February 2004) and 8·9 °C (9 December 2003). The absolute minimum 945 Polylepis at the world’s highest treeline Fig. 3. Temperatures along three soil profiles at sites with different slope aspects [north-facing (N-) and south-facing (S-) slopes] and vegetation cover (with and without canopy shadow of Polylepis). Records were taken between 9.50 and 10.20 am at 4550 m a.s.l. (25 August 2003; air temperature 5·2 °C). Fig. 2. Long-term temperature curves at the Polylepis tarapacana treeline. Above: characteristic diurnal crown air-temperature curves at 4810 m a.s.l. during three selected periods: early warm season (1– 4 November 2003); peak warm season (6–9 February 2004); peak cold season (4 – 7 July 2004). Air temperatures were measured in full canopy shade. Note that temperatures < −5 °C were not recorded. Below: rootzone temperatures (−10 cm) under full canopy shade (mean of two independent measurements between 25 August 2003 and 1 September 2004 at 4780 and 4810 m a.s.l.). Black curve, daily mean temperatures; grey area, daily temperature amplitudes (diurnal minimum and maximum temperatures). Histogram shows frequency distribution of daily mean soil temperatures across the growing season. © 2005 British Ecological Society, Functional Ecology, 19, 941–951 daily mean soil temperature for the entire year was 0·4 °C, recorded on 14 July 2004. Diurnally and annually, the canopy air temperatures at the treeline oscillated at a much greater amplitude than soil temperatures (Fig. 2). During the afternoon air temperatures, which were always recorded in full shade, regularly reached more than 20 °C on sunny days, mainly during the growing season, but also on warmer days from May to September (Fig. 2). The wet period from the end of December to the beginning of March was characterized by quite cold canopy temperatures (mean 4·2 °C) and a strongly reduced daily amplitude, with night-time minimum temperatures rarely below 0 °C. Freezing temperatures during at least 1 h per day were recorded on 303 days, hence night-time freezing within the canopy occurred almost every day except during the middle of the wet season. Hourly temperature minima below −5 °C were measured on 91 days, and on 16 days the daily mean crown air temperature was below 0 °C. The soil temperature profiles on south- and northfacing slopes clearly revealed strong slope effects, with morning temperatures below 5 cm being ≈6 K higher on north-facing slopes, where P. tarapacana grows (Fig. 3). Soil temperatures under P. tarapacana and under grass tussocks on the north-facing slope revealed no differences near the surface, but soils under trees were ≈1 K colder below 20 cm soil depth (Fig. 3). Stand density (here defined as number of trees >5 cm ha−1), as well as the basal stem area per hectare, were highest at the middle stand and lowest at the treeline (Table 1). The relative frequencies of tree-height classes show that the smallest height class (0·05–0·5 m) accounted for the largest fraction (between 22 and 38%) at all three altitudes, indicating successful regeneration across the entire transect (Fig. 4). Surprisingly, the uppermost stand was particularly rich in tiny (<5 cm) Polylepis seedlings (not included in the demographic survey) and exhibited the most pronounced pyramid-shaped height-class distribution, which may point towards regular regeneration success at the treeline. We cannot exclude that herbivory had affected the patterns found, although we saw no browsing damage, but trampling by llamas, alpacas and humans may have diminished the number of small seedlings at the lower sites. The average tree height of adult trees (>1 m high) decreased significantly by one-third from the lowest to the uppermost site, while there was no significant change in average stem diameter with elevation (Fig. 5). The mean tree-ring width in the cored (>2 m) trees decreased towards the treeline by 20% (Fig. 5), but due to the large interannual variations in tree-ring growth within a single stem (from ≈0·1–3 mm year−1), as well as the large within-site differences among tree individuals, this reduction of annual increment was not significant across the transect. However, sapwood density increased significantly with altitude by almost 946 G. Hoch & C. Körner Fig. 4. Frequency distributions of tree-height classes of Polylepis tarapacana stands at three different altitudes across the treeline ecotone. Numbers of trees measured (n) are given. Numerous tiny seedlings of P. tarapacana were found at the uppermost site but were not counted for the demographic survey. 10%, probably as a consequence of the reduced treering widths at the highest elevation (Fig. 5). As the altitudinal trend of stem diameter paralleled that of mean tree-ring width, the mean stem age of the largest trees is approximately the same at all sites along the transect. A coarse estimate revealed ages between 130 and 160 years, but rootstocks may be much older. Neither SLA nor leaf-volume density changed significantly with elevation, although SLA tended to decrease towards the treeline (Fig. 5). The annual increment of leading shoots did not differ between the lowest and the middle stand, but was significantly smaller for the uppermost trees for both growing seasons investigated (2001/02 and 2002/03; Fig. 6). The decrease in shoot growth between the lowest and the uppermost stand was more pronounced for the 2001/02 growing season (−40%) than for the 2002/ 03 season (−25%). - , © 2005 British Ecological Society, Functional Ecology, 19, 941–951 Irrespective of altitude and tree organ, low molecularweight carbohydrates accounted for the largest fraction of NSC (Fig. 7). The starch fraction of the NSC pool was smallest in branch sapwood (17% of total NSC pool) and highest in stem sapwood (32%). Within the low molecular-weight carbohydrate fraction, the sugars analysed by the NSC method (glucose, fructose and sucrose) covered >90% of the total pool in all organs (Fig. 7). In addition to the three sugars mentioned above, only raffinose and the cyclitol myo-inositol were present at concentrations measurable by gas chromatography. Other carbohydrates such as galactose and stachyose were detectable in traces, while sorbitol was completely lacking in all samples investigated. Fig. 5. Tree-growth parameters of Polylepis tarapacana at three altitudes along the transect. (a) Mean tree height (n = 15 –32 per altitude) and stem diameter (n = 8 per altitude); (b) mean sapwood density and tree-ring width (n = 8 per altitude); (c) specific leaf area (SLA) and leaf density (n = 10 per altitude). Different letters show significant differences at the 0·05 level by the Tukey–Kramer test. The altitudinal differences in NSC, as expressed on a dry mater basis, were generally small in all three organs investigated (Fig. 8). Free sugars increased with elevation in all organ types (significant in leaves and branch sapwood but not in stem sapwood; Table 2). The smaller starch fractions decreased from the lowest to the highest site (not significant in leaves; Table 2). The combination of both compound groups (NSC) resulted in a significant increase with elevation in leaves, and no significant difference in branches and stem sapwood (Fig. 8; Table 2). When expressed on a volume rather than a dry matter basis (avoiding the bias introduced by tissue density differences), the overall NSC trends with altitude did not change (Fig. 8). However, as the wood density increased significantly towards the treeline, NSC 947 Polylepis at the world’s highest treeline Fig. 6. Mean length of annual shoot growth of Polylepis tarapacana across the altitudinal transect for the growing seasons 2001/02 and 2002/03 (n = 15 shoots per elevation). Different letters show significant differences (P < 0·05) among the altitudinal categories for each season. Drawing (right) shows terminal 2-years increments of a P. tarapacana shoot. concentrations in stemwood on a volume basis were enhanced in the uppermost trees relative to the lowest site (Table 2). Even in leaves, in which volume density did not change significantly across the transect (Fig. 5), the increase in NSC concentrations with elevation became more pronounced on a leaf-volume basis than on a leaf dry matter basis (Table 2). Total lipid concentrations were low compared with NSC, and hardly exceeded 0·5% DM in branch and stem sapwood. Neither the twofold altitudinal increase of lipid concentrations in branchwood, nor the altitudinal decrease of lipids by 30% in stem sapwood, was significant when expressed as % DM (Fig. 9). However, when accounting for the increased wood density of trees at the tree limit, the lipid concentrations in branchwood were significantly higher at the uppermost site on a volume basis (Fig. 9). Total leaf N concentrations increased significantly with elevation on a dry matter basis, but only insignificantly when calculated per unit leaf volume (mg N cm−3; Fig. 10). Stable C isotope data for leaves of P. tarapacana sampled between 4320 and 4810 m a.s.l. revealed an Fig. 7. Relative proportion of (a) starch and free sugars within the whole non-structural carbohydrate (NSC) pool; (b) sugars within the low molecular-weight sugar pool in different organs of Polylepis tarapacana. Glc, glucose; Fru, fructose; Sacc, sucrose; Raff, raffinose; myo-I, myo-inositol. Values are means across all three altitudinal categories (n = 30 for leaves and branches; n = 24 for stem sapwood). altitudinal increase of δ13C, reaching from −23·9‰ at the lowest site to −23·3‰ at the treeline. The calculated linear regression is δ13C = −28·13 + 0·00104 × altitude (r2 = 0·699), which yields an approximate 1·0‰ increase per altitudinal km, and a hypothetical sea-level reference of −28·13‰. Discussion The mean 5·4 °C growing season soil temperature measured in the current study at the upper edge of the Sajama treeline ecotone matches well with the worldwide pattern described previously (Körner 2003). For instance, an average growing season mean temperature of 5·4 °C was measured at different treelines on Mexican volcanoes, 19° N (Hoch & Körner 2003). Tropical and subtropical treelines (with mean growing season temperatures of 5–6 °C) generally appear to operate at temperatures 1–2 K cooler than temperate and boreal zone treelines (≈7 °C growing season mean temperatures), which led to a global mean for 46 treelines of 6·7 ± 0·8 °C (Körner & Paulsen 2004). The treeline Table 2. Relative differences of non-structural carbohydrate (NSC) concentrations between the lowest and uppermost sampling sites, and results of an for elevation effects on NSC concentrations among all three altitudes. Results for each organ are given as percentage dry matter (% DM) and mg per volume Plant part Leaves Parameter df (% DM) 2 2 (mg cm−3) Branches (% DM) 2 (mg cm−3) 2 © 2005 British Stemwood (% DM) 2 Ecological Society,(mg cm−3) 2 Functional Ecology, Significant 19, 941–951differences (P < 0·05) are in bold. Sugars Starch Non-structural carbohydrates Difference Difference Difference (%) F P (%) F P (%) F P +22 +27 +19 +30 +3 +13 7·0 9·5 5·9 6·0 0·4 1·2 0·004 0·001 0·047 0·007 0·657 0·335 −15 −12 −36 −30 −49 −44 1·0 0·8 7·4 6·0 4·0 3·2 0·369 0·466 0·003 0·007 0·036 0·063 +10 +15 +5 +15 −19 −11 5·7 7·0 0·5 1·9 1·8 0·8 0·009 0·004 0·641 0·171 0·192 0·465 948 G. Hoch & C. Körner Fig. 8. Concentrations of non-structural carbohydrates (NSC) in leaves, branch sapwood and stem sapwood of Polylepis tarapacana along the altitudinal transect (n = 10 for leaves and branches; n = 8 for stem sapwood). Values are given as percentage dry matter (left) and as mg cm−3 of the respective tissue (right). Different letters show significant differences at the 0·05 level among altitudes by the Tukey– Kramer test. Note the different y axes. Fig. 9. Lipid concentrations in stem and branch sapwood of Polylepis tarapacana at the three altitudes of the transect (n = 10 for branches; n = 8 for stems). Values are given as percentage dry matter and as mg cm−3. Different letters show significant differences (P < 0·05) among altitudes by the Tukey–Kramer test. of Nevado Sajama is not an exception from other subtropical or tropical treelines, and thermally fits the global patterns. Other environmental factors may modulate year-to-year growth variations, but in the light of these data, effects other than those by temperature seem irrelevant for the actual position of the uppermost trees in this area. For instance, Morales et al. (2004) had shown that moisture availability can influence annual tree-ring width in the Andes, but moisture is certainly not the decisive factor for the rather abrupt Polylepis treeline, for several reasons. (1) There is no indication of water stress in δ13C data from P. tarapacana leaves. The measured δ 13C increase of 1·0‰ km−1 does not deviate from the elevational gradients found in a global survey, which revealed an average of +1·2‰ km−1 for a within-species comparison of 12 herbaceous plants, and +0·9‰ km−1 for an interspecific comparison of 25 tree species (Körner et al. 1988). (2) Despite the low annual precipitation of ≈330 mm, we found soils moist at 30 cm below the surface at the end of the dry season. Similar situations are reported for sites above 4200 m a.s.l. in Argentina (Körner 2003), and reflect a combination of low potential evapotranspiration and storage of runoff from higher elevations. Functionally humid and mesic climates are abundant at annual precipitations well below 350 mm at high altitudes and latitudes (Walter & Breckle 1994). (3) Polylepis tarapacana reaches the highest altitudes on warm and dry equator-facing slopes, with no trees on the more humid, poleward-facing slopes. If the trees’ distribution were water-limited, we would expect them to be restricted to the cooler, south-facing slopes. Crown air temperatures revealed characteristic patterns of the subtropical alpine climate, with harsh conditions for prostrate growing at the treeline. First, on more than 80% of days recorded, night-time air temperatures fell below 0 °C. Rada et al. (2001) pointed out that P. tarapacana is probably frost-tolerant during the major part of the year, but may switch to frost avoidance by accumulating low molecular-weight © 2005 British Ecological Society, Functional Ecology, 19, 941–951 949 Polylepis at the world’s highest treeline Fig. 10. Altitudinal trend of total leaf nitrogen concentrations in 1-year-old leaves of Polylepis tarapacana along the transect. Values are given as percentage dry matter and as mg cm−3. Different letters show significant differences (P < 0·05) among altitudes by the Tukey–Kramer test. © 2005 British Ecological Society, Functional Ecology, 19, 941–951 sugars at the peak warm and wet season (January and February), when temperatures rarely fall below freezing. On the other hand, as the coldest nights occur when skies are clear, they are generally followed by the warmest daytime temperatures, resulting in extreme high diurnal amplitudes between minimum and maximum air temperatures, which can reach more than 30 K. The very high afternoon canopy air temperatures measured in the current study probably resulted from special microclimatic properties of Polylepis crowns, which may trap heat fluxes from the surrounding bare soils. It has been shown for Polylepis sericea stands that mean air temperatures within the forests are generally above that of the free atmosphere (Goldstein, Meinzer & Rada 1994). The high temperature difference between north- and south-facing slopes (>6 K) underlines the significance of slope exposure. Braun (1997) reported similar exposure effects for Nevado Sajama at 4500 m a.s.l., where the temperature difference even increased towards late afternoon. According to Braun, the distribution of P. tarapacana is related to moisture on a very broad geographic scale across the Western Cordillera, while on a local scale its distribution is predominantly driven by solar irradiance and slope aspect, with trees clearly restricted to the warmer and presumably even drier sites. Such pronounced slope exposure effects on treeline position and soil temperature are rare, and seem to reflect the largely bare volcanic ground and the very steep slopes. With less steep terrain and denser ground cover, no direction effect on treeline position was found on Mexican volcanoes (Beaman 1962) or in the Alps (Paulsen & Körner 2001; Körner & Paulsen 2004). Further, no clear slope effect on the distribution of P. sericea trees was found in the Venezuelan Andes (Goldstein et al. 1994). Tree seedling mortality exceeding that of other taxa due to frost events during the growing season has been discussed as a primary determinant of treeline position at high altitudes (Smith et al. 2003; Wang et al. 2004), although there is no evidence that trees are less capable than other life forms of resisting low temperatures (Sakai & Larcher 1987). The analyses of tree height along the current transect revealed that the smallest (<0·5 m) tree height class is most abundant. Provided that tree height correlates at least loosely with tree age, this points at a dominance of young trees at all three elevations, most pronounced at the highest site. The ‘healthy’ demographic pyramid at 4810 m a.s.l. suggests constant recruitment events and sufficient seedling survival during the past decades. Additionally, numerous tiny seedlings were found at the uppermost site but not at the lower elevations. Hence it seems highly unlikely that a lack of seedlings determined the treeline on Nevado Sajama. Similarly, Byers (2000) described high seedling numbers and good regeneration of a subalpine Polylepis forest in the upper Pisoc Valley in Peru. The critical constraints must affect later life stages, when trees transform from shrub to tree stature and the apical meristems protrude from the warmer air layer near the soil surface, coupling crown temperatures more closely to the climatic conditions of the free atmosphere (Grace & Norton 1990). Accordingly, annual shoot growth in mature P. tarapacana crowns was small, and trees higher than 3·5 m were absent at the uppermost site in the current study. The comparatively low starch concentrations found in all tree organs and sites may reflect the time of sampling near the end of the cold-dry season. Temperate evergreen conifers, for example, also exhibit lowest starch concentrations towards the end of the dormant season, but a pronounced starch accumulation immediately prior to the flushing of new shoots (Schaberg et al. 2000; Hoch, Richter & Körner 2003). Similarly to our study, Rada et al. (2001) found free sugar concentrations to be more than three times higher than the concentrations of starch in leaves of P. tarapacana at the beginning of September. The complete absence of sorbitol in P. tarapacana is in line with previous findings of Wallaart (1980), who described this sugar alcohol to be lacking in most phylogenetic tribes of the subfamily Rosoideae (which includes the genus 950 G. Hoch & C. Körner © 2005 British Ecological Society, Functional Ecology, 19, 941–951 Polylepis), while it resembles an important form of C transport in all other subfamilies within the Rosaceae. There was no evidence for a depletion of mobile C pools in P. tarapacana with altitude. Although the differences in NSC and lipid concentrations were small, and most of the time insignificant, among the sites, we found significantly higher concentrations of NSC in leaves and lipids in branches at the uppermost elevation. Because NSC, as well as lipids, decrease from the youngest tree rings towards the pith in heartwoodforming trees (Magel et al. 1997; Piispanen & Saranpää 2002), the sampling procedure used for the current study probably influenced the elevational trends in the stemwood of P. tarapacana. At all three elevations, stem sapwood was sampled as the outer 1·5 cm stem core segment. Thus the slightly greater tree-ring width at lower elevations may have contributed to the (not significant) NSC reduction in stem sapwood towards the treeline. In branchwood tissue, which was exactly 5 years old at each elevation, the mobile C pools tended to increase towards the treeline. The evidence that mobile C compounds are not becoming increasingly rare in tissues of P. tarapacana at the tree limit does not support the C-limitation hypothesis (Stevens & Fox 1991; Johnson, Germino & Smith 2004). In a recent study, low but clearly positive net photosynthetic rates were measured in both the dry and the cold season for P. tarapacana growing at 4300 m a.s.l. at Nevado Sajama (Garcia-Nunez et al. 2004). Goldstein et al. (1994) and Rada et al. (2001) demonstrated strongly positive net assimilation rates of P. sericea at its upper distribution limit in Venezuela, making C shortage for this species highly unlikely. Plants at high altitudes operate at very high photosynthetic capacity, and thus, together with increased diffusivity, compensate for the elevational reduction of partial CO 2 pressure (Körner 2003). Previous studies revealed no change in maximum photosynthetic rates at local partial pressure of CO2 over 2– 4 km elevation (Körner & Diemer 1987; Terashima et al. 1995). It seems more likely that growth drops so abruptly, and thus leads to the altitudinal tree limit, because temperatures fall too low for meristematic activity (sink limitation). The results are therefore in line with previous studies at northern hemisphere climatic treelines at different latitudes, all of which revealed increasing C-charging of tree tissue with increasing altitude (Hoch & Körner 2003; Shi 2005). The small altitudinal increase of N concentration in leaf tissue follows global trends (Körner 1989; Mitchell et al. 1999), and seems to be associated with enhanced photosynthetic capacity at high elevations (Körner & Diemer 1987). In conclusion, we found no evidence that the ‘worldrecord’ treeline elevation of P. tarapacana at Nevado Sajama is the result of increasing C shortage, water limitation or recruitment problems at high elevations. The mean 5·4 °C soil temperature during the growing season places this treeline perfectly within the thermal range of other tropical and subtropical treelines worldwide, which occur at lower altitudes (Körner & Paulsen 2004). The reason why P. tarapacana reaches such exceptional elevations in this part of the Andes is associated with the regional climatic peculiarities (e.g. the ‘Massenerhebungseffect’, low degree of cloudiness, solar warming of the bare volcanic soils). 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Received 18 April 2005; revised 1 July 2005; accepted 4 July 2005
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