Next Article in Journal
Comparison of Natural Regeneration in Natural Grassland and Pine Plantations across an Elevational Gradient in the Páramo Ecosystem of Southern Ecuador
Next Article in Special Issue
Artificial Top Soil Drought Hardly Affects Water Use of Picea abies and Larix decidua Saplings at the Treeline in the Austrian Alps
Previous Article in Journal
New Ensemble Models for Shallow Landslide Susceptibility Modeling in a Semi-Arid Watershed
Previous Article in Special Issue
High Resolution Maps of Climatological Parameters for Analyzing the Impacts of Climatic Changes on Swiss Forests
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Weak Apical Control of Swiss Stone Pine (Pinus cembra L.) May Serve as a Protection against Environmental Stress above Treeline in the Central European Alps

1
Department of Botany, Leopold-Franzens-Universität Innsbruck, Sternwartestraße15, A-6020 Innsbruck, Austria
2
Department of Alpine Timberline Ecophysiology, Federal Research and Training Centre for Forests, Natural Hazards and Landscape (BFW), Rennweg 1, A-6020 Innsbruck, Austria
*
Author to whom correspondence should be addressed.
Forests 2019, 10(9), 744; https://doi.org/10.3390/f10090744
Submission received: 31 July 2019 / Revised: 22 August 2019 / Accepted: 27 August 2019 / Published: 28 August 2019
(This article belongs to the Special Issue Alpine and Polar Treelines in a Changing Environment)

Abstract

:
At the treeline in the Central European Alps, adverse climate conditions impair tree growth and cause krummholz formation of Swiss stone pine (Pinus cembra L.). Multi-stemmed trees (tree clusters) are frequently found in the treeline ecotone and are generally thought to originate from seed caches (multiple genets) of the European nutcracker (N. caryocatactes) or due to repeated damage of the leader shoot by browsing or mechanical stress (single genet). Additionally, lack of apical control can lead to upward bending of lateral branches, which may obscure single-genet origin if the lower branching points are overgrown by vegetation and the humus layer. The multi-stemmed growth form may serve as a means of protection against extreme environmental stress during winter, especially at wind-exposed sites, because leeward shoots are protected from, e.g., ice particle abrasion and winter desiccation. The aims of this study therefore were to analyze in an extensive field survey: (i) whether weak apical control may serve as a protection against winter stress; and (ii) to what extent the multi-stemmed growth form of P. cembra in the krummholz zone is originating from a single genet or multiple genets. To accomplish this, the growth habit of P. cembra saplings was determined in areas showing extensive needle damage caused by winter stress. Multi-stemmed saplings were assigned to single and multiple genets based on determination of existing branching points below the soil surface. The findings revealed that upward bending of lateral branches could protect saplings against winter stress factors, and, although multi-stemmed P. cembra trees were primarily found to originate from multiple genets (most likely seed caches), about 38% of tree clusters originated from upward bending of (partially) buried branches. The results suggest that weak apical control of P. cembra in the sapling stage might be an adaptation to increase survival rate under severe climate conditions prevailing above treeline during winter.

1. Introduction

The alpine treeline is a conspicuous climate-driven ecological boundary, which designates the upper elevational limit of tree growth [1,2,3]. There is extensive evidence that at high altitude cold temperatures during the growing season, which directly limit cell division and differentiation in meristematic tissues (“carbon-sink-limitation hypothesis”), are a major cause of treeline formation [4,5,6,7]. Above the treeline, adverse climatic conditions (e.g., frost drought, wind abrasion, and late frosts) frequently occur such that height growth of trees is strongly suppressed and tree stature is dominated by stunted multi-stemmed architecture (krummholz).
Swiss stone pine (Pinus cembra L.) is a key species forming the alpine treeline in the Central European Alps [8], which is reached at about 2400 m–2500 m above sea level (a.s.l.) under natural conditions, i.e., without human interference [3]. The heavy wingless seeds of P. cembra are almost exclusively dispersed by the European nutcracker (Nucifraga caryocatactes L.). At sheltered sites, krummholz forms of this species may be found up to ca. 2800 m a.s.l. (see [9]). Three growth forms of P. cembra can be distinguished: (1) single-trunk; (2) single genet multi-trunk caused by repeated damage of the leader shoot; and (3) multi-genet tree cluster attributable to multiple germination of seed caches [10]. The latter two forms are morphologically similar and generally thought to be distinguishable only by genetic analysis [11]. Although several coniferous tree species, e.g., spruces, firs, and larches, are able to form clonal tree groups by layering, i.e., formation of adventitious roots on buried lateral branches [12,13,14], cluster formation by vegetative sprouting has not been reported to occur in P. cembra [2,3]. Most pine species have a dominant main stem and distinct lateral branches which grow shorter and more horizontal than the vertical leader shoot [15], i.e., strong apical control is exerted by the leader shoot. Lack of apical (hormonal) control, e.g., due to mechanical or biotic damage of the leader, leads to upward bending of branches [16]. Shoot architecture of P. cembra is generally characterized by a vertical main trunk and upward bending of lateral branches.
This study aimed to increase our understanding of tree adaptation to extreme environmental conditions prevailing in the treeline ecotone. There are no reports on the influence of apical control on resistance against environmental stress in the treeline ecotone. Therefore, in an extensive field survey, we evaluated whether weak apical control may protect P. cembra against winter stress (frost desiccation, and snow mold). Furthermore, determining a morphological feature that consistently distinguishes single genet multi-trunk trees from multi-genet tree clusters originating from seed caches was a second aim of this study.

2. Materials and Methods

The study area is situated in the treeline ecotone on Mt. Patscherkofel (2246 m a.s.l.; 47°12′ 33″ N; 11°27′40″ E), which is located in the Central European Alps in western Austria. Mean annual temperature and precipitation (1967–2015) at the top of Mt. Patscherkofel are 0.2 °C and 883 mm with minimum in winter (December–February: 139 mm), respectively. The geology is dominated by gneisses and shist. Three sites (based on information gathered in Table 1) were selected on a ridge facing W to WNW (slope 15°–20°) above the current treeline at ca. 2100 m–2150 m a.s.l. Selected sites are frequently exposed to extreme winds (foehn), frequently reaching >100 km/h. Exposed mineral soil is common and dominating plants (Loiseleuria procumbens (L.) Desv., Calluna vulgaris (L.) Hull., Juncus trifidus L. and lichens, e.g., Thamnolia vermicularis (Sw.) Ach.ex Schaer and Alectoria ochroleuca (Hoffm.) A. Massal) are known to be resistant against wind, frost and winter desiccation [8].
The study was conducted on P. cembra, which is the dominant and widespread conifer along the treeline ecotone. European larch (Larix decidua Mill.) is scattered at some locations. The importance of apical control in P. cembra saplings as a mean to protect against winter stress was studied at wind exposed ridges and depressions with a long duration of snow cover showing pronounced needle damage after winter. In each of the three sites, one 100 m2 plot was established where all P. cembra saplings (single stemmed and clusters, i.e., multi-stemmed trunks) without any visible damage to the leader shoot were counted. Multi-stemmed trunks were assigned to single and two or more genets by digging out all leaders until able to be traced back to the main stem and determining whether below the soil surface upward bending of lateral branches (i.e., single genet) or vertical leader shoots originating from seed caches (i.e., multi-genets) occurred.
Differences in the overall mean number between single stemmed and multi-stemmed P. cembra individuals were analyzed by one-way analysis of variance (ANOVA). One-way ANOVA was also used to test for differences between multi-genet and single genet saplings. A probability level of p < 0.05 was considered as statistically significant. Statistical analyses were made with the SPSS 16 software package for windows (SPSS, Inc., Chicago, IL, USA).

3. Results

Stem height and diameter of selected saplings (n = 92) were 39.2 ± 22.4 cm and 1.9 ± 1.2 cm, respectively, and annual shoot growth amounted to 4.4 ± 1.4 cm (mean values ± standard deviation). These growth variables were not significantly different among single-stemmed and multi-stemmed saplings. A potentially protective function of weak apical control in P. cembra against severe winter drought is depicted in Figure 1 and Figure 2. Several examples of upward bending lower branches with connection to the main stem below the soil surface, whose vertical growing lateral branches are obscured by the humus layer and intensively growing dwarf-shrubs (L. procumbens, C. vulgaris), are depicted in Figure 3.
Above the treeline, the number of single stemmed P. cembra individuals (9 ± 3) was significantly lower (p = 0.02) when compared to the number (22 ± 2) of multi-stemmed P. cembra saplings, which corresponds to 28 ± 8% and 72 ± 8% single- and multi-stemmed P. cembra saplings, respectively (Table 1). The multi-stemmed growth form originates from 14 ± 6 (62 ± 19%) seed caches from multiple genet individuals and 8 ± 5 (38 ± 19%) seed caches from upright growing branches, i.e., single genet individuals (Table 1), which however was not statistically significant (p = 0.19). Upward-bending branches of a P. cembra sapling growing in a depression with long-lasting snow cover and frequent occurrence of snow mold is shown in Figure 4.

4. Discussion

4.1. Multi-Stemmed Growth Form

Multi-stemmed trunks of P. cembra are frequently occurring in the alpine treeline ecotone [11,17,18]. This growth form is frequently reported to result from seed caches [11,19] or damage of the leader shoot caused by browsing or mechanical disturbance (e.g., winter desiccation, wind abrasion, frost, and avalanche [2,20]). In the case of destroyed apical meristems, apical control is lost and lateral branches bend upwards and form vertical shoots [16]. Here, we report that, in about 38% of multi-stemmed P. cembra saplings, lower branches at the base of the stem tend to grow upright without any visible damage to the leader. Hence, weak apical control may exist in P. cembra at the sapling stage, which can be explained by the competitive-sink hypothesis developed in [21]. This hypothesis states that branches compete with the subjacent stem for branch-produced carbohydrates, i.e., when the subjacent stem sink for carbohydrates is small, as is to be expected at the sapling stage, the branch is largely released from apical control and develops vertical growth.
At wind-exposed ridges, tree cluster formation favors growth of dwarf-shrubs (especially L. procumbens and C. vulgaris) by locally trapped litter and wind-blown organic and soil particles, which may increase nutrient content and water storage capacity of the soil [2]. Because the branching point close to the soil surface may be overgrown by vegetation and development of a humus layer, the origin from a single genet can be obscured. By carefully removing vegetation and the humus layer, multi-stemmed trunks of saplings and small trees can unequivocally be allocated to lateral branches of a main stem (single genet) or genetic different individuals (multi genet) originating from seed caches. Multi-stemmed trunks merge with time, which survive and grow better than single-stemmed trees, most likely due to better structural stability against wind [11,22,23]. Upright branches will ultimately merge with increasing tree age and radial growth, forming multi-stemmed trees, which—without genetic analysis—can mistakenly be assigned to originate from multi genet seed caches.
Analyzing the genetic diversity in multi-stemmed P. cembra, the authors of [11,23] found that 7 out of 22 and 1 out of 4 P. cembra tree clusters, i.e., 30% and 25%, respectively, were single genet multi-stemmed trees. Their findings are quite similar to our morphological approach, which was based on determination of the branching pattern below the soil surface. Hence, the assumption of a genetically controlled delay in dormancy release from varying stem diameter in multi-stemmed clusters may be false, because multi-genet shoots can be hidden by upright growing branches belonging to the same single genet tree individual.

4.2. Protective Function of Cluster Formation and Weak Apical Control During Tree Establishment

In the alpine treeline ecotone, natural regeneration of P. cembra is concentrated on locally higher terrain, such as ridges, shoulders and rock buttresses where wind exposure is high, snow depth is low, snow cover duration is short and there is sparse vegetation. Tree seedling establishment is controlled by micro-relief and/or shelter from low stature alpine vegetation, e.g., dwarf shrubs [24,25]. Once seedlings emerge from the ground vegetation and are exposed to the convective conditions of the atmosphere, wind effects on exposed ridges are important for tree survival during winter [3,12,17]. Damage of needles and buds is common at wind-exposed sites with little snow cover due to injuries from abrasive blowing snow, ice and mineral particles (for review see [26]), which reduces cuticle resistance leading to winter desiccation. Winter desiccation results from gradual water loss through transpiration, which cannot be compensated due to deep and long-lasting soil frost at snow-free ridges [27,28,29]. Saplings growing in clusters or single genet trees with multi-stemmed trunks caused by weak apical control create a wind-barrier effect that reduces mechanical damage at the sheltered leeward side especially during winter. This is corroborated by the finding that afforestation of P. cembra in groups in the subalpine zone yielded greater success than planting solitary trees ([30]; for a review, see [31]). Tree groups produce a snowdrift at their leeward side, which prevents deep soil frost and provides soil moisture at the beginning of the growing season [19]. On the other hand, weak apical control is also favorable for tree establishment in snow-rich concave topography and leeward slopes. Here, lower branches are less likely to be at risk for occurrence of snow mold under a long-lasting snow cover, if lower branches grow upright in the early sapling stage. Age- and/or size-related changes in apical control are to be expected, however, as a tree faces different challenges to survival with increasing tree age and/or size (cf. [32]). Hence, findings of this study suggest that upward bending of basal branches, i.e., a weak apical control in the sapling stage, might be an adaptation to extreme environmental conditions prevailing in the alpine treeline ecotone in cool temperate and boreal mountains, especially during winter. Our interpretation is corroborated by strong apical control found in co-occurring European larch (L. decidua [33]), which, due to its deciduous behavior, is less prone to winter drought and snow mold.

5. Conclusions

The results of this field survey suggest that cluster formation due to weak apical control of lateral branches at the stem base might be an adaptation to extreme environmental conditions prevailing above treeline within the study area. About one third of multi-stemmed P. cembra clusters in the krummholz zone belonged to a single genet. Multi-stemmed trees serve as protection against winter stress factors (snow and ice particle abrasion, and winter desiccation), have a better structural stability against wind and possibly improve resource acquisition due to trapping of litter and wind-blown soil. However, as this study was carried out within the inner Alpine dry zone of the Central European Alps, where the local climate is strongly influenced by southern “Foehn” type winds [34], further research needs to clarify the above demonstrated growth patterns of P. cembra saplings at sites differing in environmental conditions, especially winter stress.

Author Contributions

W.O. designed the study. W.O., T.A.G. and F.B. contributed to data acquisition. W.O., T.A.G. and G.W. interpreted and discussed the data. W.O. and G.W. wrote the manuscript.

Funding

This research received no external funding.

Acknowledgments

The authors thank two anonymous reviewers for their comments on earlier versions of the manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Wieser, G.; Tausz, M. Trees at Their Upper Limit: Treelife Limitations at the Alpine Timberline; Springer: Dordrecht, The Netherlands, 2007. [Google Scholar]
  2. Holtmeier, F.K. Mountain Timberlines: Ecology, Patchiness, and Dynamics. In Advances in Global Change Research; Springer: Berlin, Germany, 2009; Volume 36, p. 437. [Google Scholar]
  3. Körner, C. Alpine Treelines: Functional Ecology of the Global High Elevation Tree Limits; Springer: Basel, Switzerland, 2012; p. 220. [Google Scholar]
  4. Körner, C. A re-assessment of high elevation treeline positions and their explanation. Oecologia 1998, 115, 445–459. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  5. Grace, J.; Berninger, F.; Nagy, L. Impacts of climate change on the tree line. Ann. Bot. 2002, 90, 537–544. [Google Scholar] [CrossRef] [PubMed]
  6. Oberhuber, W. Influence of climate on radial growth of Pinus cembra within the alpine timberline ecotone. Tree Physiol. 2004, 24, 291–301. [Google Scholar] [CrossRef] [PubMed]
  7. Körner, C.; Paulsen, J. A world-wide study of high altitude treeline temperatures. J. Biogeogr. 2004, 31, 713–732. [Google Scholar] [CrossRef]
  8. Ellenberg, H.; Leuschner, C. Vegetation Mitteleuropas mit den Alpen: In Ökologischer, Dynamischer und Historischer Sicht; Verlag Eugen Ulmer: Stuttgart, Germany, 2010. [Google Scholar]
  9. Available online: https://www.lfi.ch/resultate/meldungen/logbuch.php (accessed on 12 July 2019).
  10. Linhart, Y.B.; Tomback, D.F. Seed dispersal by nutcrackers causes multi-trunk growth form in pines. Oecologia 1985, 67, 107–110. [Google Scholar] [CrossRef] [PubMed]
  11. Tomback, D.F.; Holtmeier, F.K.; Mattes, H.; Carsey, K.S.; Powell, M.L. Tree clusters and growth form distribution in Pinus cembra, a bird-dispersed pine. Arct. Alp. Res. 1993, 25, 374–381. [Google Scholar] [CrossRef]
  12. Jeník, J. Clonal growth in woody plants: A review. Folia Geobot. 1994, 29, 291–306. [Google Scholar] [CrossRef]
  13. Bellingham, P.J.; Sparrow, A.D. Resprouting as a life history strategy in woody plant communities. Oikos 2000, 89, 409–416. [Google Scholar] [CrossRef]
  14. Del Tredici, P. Sprouting in temperate trees: A morphological and ecological review. Bot. Rev. 2001, 67, 121–140. [Google Scholar] [CrossRef]
  15. Turnbull, C.G. Shoot architecture II: Control of branching. In Plant Architecture and Its Manipulation; Turnbull, C.G., Ed.; Blackwell Publishing: Oxford, UK, 2005; Volume 17, pp. 92–120. [Google Scholar]
  16. Wilson, B.F. Apical control of branch growth and angle in woody plants. Am. J. Bot. 2000, 87, 601–607. [Google Scholar] [CrossRef]
  17. Tranquillini, W. Physiological Ecology of the Alpine Timberline: Tree Existence at High Altitudes with Special Reference to the European Alps; Springer: Berlin, Germany, 1979. [Google Scholar]
  18. Kratochwil, A.; Schwabe, A. Wuchsformen der Arve (Pinus cembra L.) in Abhängigkeit von der ornithochoren Ausbreitung-im Vergleich mit Weidbuchen (Fagus sylvatica L.). Diss. Bot. 1993, 196, 107–134. [Google Scholar]
  19. Holtmeier, F.K.; Broll, G. Broll Feedback effects of clonal groups and tree clusters on site conditions at the treeline: Implications for treeline dynamics. Clim. Res. 2017, 73, 85–96. [Google Scholar] [CrossRef]
  20. Schuster, W.S.; Mitton, J.B. Relatedness within clusters of a bird-dispersed pine and the potential for kin interactions. Heredity 1991, 67, 41–48. [Google Scholar] [CrossRef] [Green Version]
  21. Wilson, B.F.; Gartner, B.L. Effects of phloem girdling in conifers on apical control of branches, growth allocation and air in wood. Tree Physiol. 2002, 22, 347–353. [Google Scholar] [CrossRef] [PubMed]
  22. Till-Bottraud, I.; Fajardo, A.; Rioux, D. Multi-stemmed trees of Nothofagus pumilio second-growth forest in Patagonia are formed by highly related individuals. Ann. Bot. 2012, 110, 905–913. [Google Scholar] [CrossRef] [PubMed]
  23. Höhn, M.; Ábrán, P.; Vendramin, G.G. Genetic analysis of Swiss stone pine populations (Pinus cembra L. subsp. cembra) from the Carpathians using chloroplast microsatellites. . Acta Silv. Lign. Hung 2005, 1, 39–47. [Google Scholar]
  24. Smith, W.K.; Germino, M.J.; Hancock, T.E.; Johnson, D.M. Another perspective on altitudinal limits of alpine timberlines. Tree Physiol. 2003, 23, 1101–1112. [Google Scholar] [CrossRef] [Green Version]
  25. Renard, S.M.; McIntire, E.J.; Fajardo, A. Winter conditions—Not summer temperature—Influence establishment of seedlings at white spruce alpine treeline in Eastern Quebec. J. Veg. Sci. 2016, 27, 29–39. [Google Scholar] [CrossRef]
  26. Holtmeier, F.K.; Broll, G. Wind as an ecological agent at treelines in North America, the Alps, and the European Subarctic. Phys. Geogr. 2010, 31, 203–233. [Google Scholar] [CrossRef]
  27. Larcher, W. Frosttrocknis an der Waldgrenze und in der alpinen Zwergstrauchheide auf dem Patscherkofel bei Innsbruck. Veröffentlichungen Mus. Ferdinandeum Innsbr. 1957, 37, 49–81. [Google Scholar]
  28. Holzer, K. Winterliche Schäden an Zirben nahe der alpinen Baumgrenze. Cent. Gesamte Forstwes. 1959, 76, 232–244. [Google Scholar]
  29. Hadley, J.L.; Smith, W.K. Influence of krummholz mat microclimate on needle physiology and survival. Oecologia 1987, 73, 82–90. [Google Scholar] [CrossRef] [PubMed]
  30. Aulitzky, H.; Turner, H.; Mayer, H. Bioklimatische Grundlagen einer standortsgemäßen Bewirtschaftung des subalpinen Lärchen-Arvenwaldes. Mitt. Eidg. Anst. Forstl. Vers. 1982, 58, 327–577. [Google Scholar]
  31. Schönenberger, W. Cluster afforestation for creating diverse mountain forest structes—A review. For. Ecol. Manag. 2001, 145, 121–128. [Google Scholar] [CrossRef]
  32. Day, M.E.; Greenwood, M.S.; Diaz-Sala, C. Age- and size-related trends in woody plant shoot development: Regulatory pathways and evidence for genetic control. Tree Physiol. 2002, 22, 507–513. [Google Scholar] [CrossRef] [PubMed]
  33. Prendin, A.L.; Petit, G.; Fonti, P.; Rixen, C.; Dawes, M.A.; von Arx, G. Axial xylem architecture of Larix decidua exposed to CO2 enrichment and soil warming at the tree line. Funct. Ecol. 2018, 32, 273–287. [Google Scholar] [CrossRef]
  34. Fliri, F. Das Klima derAlpen im Raume von Tirol; Universitätsverlag Wagner: Innsbruck, Austria, 1975. [Google Scholar]
Figure 1. Pinus cembra sapling with upward-bending lateral branches (left) and P. cembra showing strong needle damage on the wind-exposed side caused by ice particle abrasion and winter desiccation, while sheltered leeward side remained largely undamaged (right).
Figure 1. Pinus cembra sapling with upward-bending lateral branches (left) and P. cembra showing strong needle damage on the wind-exposed side caused by ice particle abrasion and winter desiccation, while sheltered leeward side remained largely undamaged (right).
Forests 10 00744 g001
Figure 2. Multi-stemmed appearance of P. cembra individuals (single genet) showing strong needle damage on the wind-exposed side caused by ice particle abrasion and winter desiccation, while sheltered leeward side remained largely undamaged (left). Upright growing lower branch after vegetation and raw humus layer was removed (right).
Figure 2. Multi-stemmed appearance of P. cembra individuals (single genet) showing strong needle damage on the wind-exposed side caused by ice particle abrasion and winter desiccation, while sheltered leeward side remained largely undamaged (left). Upright growing lower branch after vegetation and raw humus layer was removed (right).
Forests 10 00744 g002
Figure 3. Examples of weak apical control of excavated basal branches of P. cembra saplings showing no damage to the leader shoot.
Figure 3. Examples of weak apical control of excavated basal branches of P. cembra saplings showing no damage to the leader shoot.
Forests 10 00744 g003
Figure 4. Branches of P. cembra in a hollow with long-lasting snow cover, where Rhododendron ferrugineum L. is the dominating shrub (left). Predominantly dead lower branches caused by snow mold. Note shoot tips with undamaged green needles (right).
Figure 4. Branches of P. cembra in a hollow with long-lasting snow cover, where Rhododendron ferrugineum L. is the dominating shrub (left). Predominantly dead lower branches caused by snow mold. Note shoot tips with undamaged green needles (right).
Forests 10 00744 g004
Table 1. Number of P. cembra individuals at a wind-exposed ridge above treeline belonging to single- or multi-stemmed growth form. Multi-stemmed growth form is divided into multi-genet individuals developing from seed caches, and single-genet individuals, which developed upright growing lower branches. Percentages are given in parenthesis. For multi-stemmed growth form the mean number of shoots ± standard deviation per site are given. Significant differences (p < 0.05) in the mean values of the three plots (± SD) between single- and multi-stemmed and between multi-genet and single genet, respectively, are marked in bold and italics.
Table 1. Number of P. cembra individuals at a wind-exposed ridge above treeline belonging to single- or multi-stemmed growth form. Multi-stemmed growth form is divided into multi-genet individuals developing from seed caches, and single-genet individuals, which developed upright growing lower branches. Percentages are given in parenthesis. For multi-stemmed growth form the mean number of shoots ± standard deviation per site are given. Significant differences (p < 0.05) in the mean values of the three plots (± SD) between single- and multi-stemmed and between multi-genet and single genet, respectively, are marked in bold and italics.
Single StemmedMulti-Stemmed
siten n shoots (mean ± SD)Multi-genetSingle genet
13111 (35)20 (65)2.9 ± 1.39 (45)11 (55)
2306 (20)24 (80)3.5 ± 1.620 (83)4 (17)
3319 (29)22 (71)2.6 ± 0.613 (59)9 (41)
Mean 9 ± 3 (28 ± 8)22 ± 2 (72 ± 8)3.0 ± 0.514 ± 6 (62 ± 19)8 ± 5 (38 ± 19)

Share and Cite

MDPI and ACS Style

Oberhuber, W.; Geisler, T.A.; Bernich, F.; Wieser, G. Weak Apical Control of Swiss Stone Pine (Pinus cembra L.) May Serve as a Protection against Environmental Stress above Treeline in the Central European Alps. Forests 2019, 10, 744. https://doi.org/10.3390/f10090744

AMA Style

Oberhuber W, Geisler TA, Bernich F, Wieser G. Weak Apical Control of Swiss Stone Pine (Pinus cembra L.) May Serve as a Protection against Environmental Stress above Treeline in the Central European Alps. Forests. 2019; 10(9):744. https://doi.org/10.3390/f10090744

Chicago/Turabian Style

Oberhuber, Walter, Theresa Andrea Geisler, Fabio Bernich, and Gerhard Wieser. 2019. "Weak Apical Control of Swiss Stone Pine (Pinus cembra L.) May Serve as a Protection against Environmental Stress above Treeline in the Central European Alps" Forests 10, no. 9: 744. https://doi.org/10.3390/f10090744

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop