The alpine dwarf shrub Cassiope fastigiata in the Himalayas: does it reflect site-specific climatic signals in its annual growth rings? Eryuan Liang, Wenwen Liu, Ping Ren, Binod Dawadi & Dieter Eckstein Trees Structure and Function ISSN 0931-1890 Volume 29 Number 1 Trees (2015) 29:79-86 DOI 10.1007/s00468-014-1128-5 1 23 Your article is protected by copyright and all rights are held exclusively by SpringerVerlag Berlin Heidelberg. This e-offprint is for personal use only and shall not be selfarchived in electronic repositories. If you wish to self-archive your article, please use the accepted manuscript version for posting on your own website. You may further deposit the accepted manuscript version in any repository, provided it is only made publicly available 12 months after official publication or later and provided acknowledgement is given to the original source of publication and a link is inserted to the published article on Springer's website. The link must be accompanied by the following text: "The final publication is available at link.springer.com”. 1 23 Author's personal copy Trees (2015) 29:79–86 DOI 10.1007/s00468-014-1128-5 ORIGINAL PAPER The alpine dwarf shrub Cassiope fastigiata in the Himalayas: does it reflect site-specific climatic signals in its annual growth rings? Eryuan Liang • Wenwen Liu • Ping Ren Binod Dawadi • Dieter Eckstein • Received: 2 May 2014 / Revised: 17 October 2014 / Accepted: 7 November 2014 / Published online: 23 November 2014 Ó Springer-Verlag Berlin Heidelberg 2014 Abstract Key message This is the first time to show that alpine Cassiope fastigiata shrubs form distinct annual growth rings and record climatic signals. Abstract Cassiope species grow as dwarf shrubs at high latitudes and high elevations. Unlike in the High Arctic, not much is known about their age and growth on the Tibetan Plateau and in the Himalayas. There, Cassiope fastigiata could potentially serve as indicator species for climate change. The objective of our study, therefore, was to investigate its dendroecological potential. For this purpose, 20 shoots were collected both on the south-eastern Tibetan Plateau (site 1) and in the central Himalayas (site 2). Crosssections of 8–10 lm in thickness were cut and the widths of the clearly distinguishable growth rings were measured. No missing outer rings were detected at the shoot base when serial sectioning was applied. Of the 40 shoots, 19 at site 1 and 10 at site 2 showed similar growth patterns. The remaining shoots were excluded from further analyses. C. fastigiata formed up to 30 annual growth rings whose width varied from 13 to 150 lm. Its growth at both sites was positively associated with temperature in late winter/ early spring, and at site 2 additionally with precipitation in late autumn of the preceding year and spring of the current year. Our study confirmed that C. fastigiata forms distinct annual growth rings. The growth response to precipitation at site 1 and the lack thereof at site 2 result from differences in hydrology between the south-eastern Tibetan Plateau and the central Himalayas. Keywords Dendroecology Growth-ring formation High altitude Treeline Tibetan Plateau Central Himalayas Introduction Communicated by A. Braeuning. E. Liang (&) W. Liu P. Ren B. Dawadi Key Laboratory of Alpine Ecology and Biodiversity, Key Laboratory of Tibetan Environment Changes and Land Surface Processes, Institute of Tibetan Plateau Research, Chinese Academy of Sciences, Beijing 100101, China e-mail: [email protected] W. Liu P. Ren University of Chinese Academy of Science, Beijing 100049, China B. Dawadi Central Department of Hydrology and Meteorology, Tribhuvan University, Kathmandu, Nepal D. Eckstein Centre of Wood Sciences, Wood Biology, University of Hamburg, Hamburg, Germany Shrubs and dwarf shrubs have wider ecological amplitudes than trees and thus are suitable bioindicators for extreme environments (Schweingruber and Dietz 2001). Moreover, shrubs and dwarf shrubs offer a unique opportunity to extend the existing dendrochronological networks into treeless plant communities (e.g., Woodcock and Bradley 1994; Forbes et al. 2010; Hallinger et al. 2010; Liang et al. 2012; Camarero et al. 2013; Schweingruber et al. 2013; Zimowski et al. 2014) and to track the influence of climate change along vegetation-range margins (Myers-Smith et al. 2011; Elmendorf et al. 2012; Pearson et al. 2013). The genus Cassiope (Ericaceae) consists of about 20 evergreen dwarf shrub species, growing in harsh environments (Fang et al. 2005). To date, dendroecological studies have mainly been focussed on C. tetragona in the High 123 Author's personal copy 80 Arctic. Various annual growth parameters of this species, such as the annual average leaf length and the annual shoot increment, have been used as high-resolution, arctic-wide climate proxy records (e.g. Callaghan et al. 1989; Rayback and Henry 2005; Rozema et al. 2009; Weijers et al. 2010, 2013). Although some evidence for a periodic growth in girth of C. tetragona shoots was noted (Rayback et al. 2012a; Schweingruber et al. 2013; Weijers et al. 2013), no ring-width chronology of this species has been developed. From Cassiope species at alpine regions, other than C. mertensiana (Rayback et al. 2012b), not much is known as to their longevity and growth. In this study, we focus on the alpine species C. fastigiata, widespread on the Tibetan Plateau and in the Himalayas (Fang et al. 2005). It often grows above the treeline. The objectives of this study were to develop ring-width chronologies and to find the climate drivers for its growth. Recent studies on, e.g., Hippophae rhamnoides, Juniperus pingii var. wilsonii and Rhododendron spp. showed that alpine shrubs recorded climatic signals in their growth rings similar to those of close-by timberline trees (Xiao et al. 2007; Liang and Eckstein 2009; Liang et al. 2012; Li et al. 2013). Similar to tree growth on the south-eastern Tibetan Plateau (Liang et al. 2009) and in the central Himalayas (Liang et al. 2014), the growth of C. fastigiata may respond differently to the differing climatic conditions at both sites. Materials and methods Dwarf shrub species studied, sampling sites and regional climate C. fastigiata grows from 3,000 to 4,500 m a.s.l. in Yunnan and Tibet, China, and along the southern Himalayas such as in Pakistan, India, Nepal and Bhutan. It is an evergreen dwarf shrub of up to 30 cm high, preferring open and Trees (2015) 29:79–86 sunny sites. Its leaves and bell-like flowers are similar to those of the circumarctic dwarf shrub C. tetragona. The thick, lance-like, leaves are up to 5 mm long, and several shoots are usually clustered together (Fig. 1). We selected two sampling sites, approximately 800 km apart, representing the northern and southern distribution margins of C. fastigiata (Fig. 2). The growing period was assumed to last from May to August/September. Site 1 is located on the south-eastern Tibetan Plateau where C. fastigiata grows just above the Juniperus saltuaria treeline (4,400 m a.s.l.) on a south-facing slope covered by Rhododendron shrubs (up to 3 m high) up to 70 % and by C. fastigiata up to 10 %; the soil is podzolic. Close to site 1, an automatic weather station (AWS) is in operation since November 2006 (Liu et al. 2011). From 2007 to 2013, the annual mean temperature ranged from -0.2 to 0.9 °C. The mean temperature for the coldest (January) and warmest month (July) were -8.0 ± 1.7 and 7.9 ± 0.5 °C, respectively. In extreme cases, temperature may drop down to 18 °C. The mean annual sum of precipitation amounted to 957 mm, of which 62 % fell during the monsoon season (June–September). Snowfall mainly occurred between November and May. Site 2 is located 10 km south of the Mt. Everest in the Khumbu Valley of the central Himalayas and 150 km northeast of Kathmandu (1,369 m a.s.l.). There, C. fastigiata occurs just above the Betula utilis treeline (4,150 m a.s.l.) [close to site SKB1 in Liang et al. (2014)] in an open terrain on a northwest-facing slope. Here, up to 30 cm high Rhododendron anthopogon and C. fastigiata, which together cover 20–30 % of the area, are dominant on a thin layer of rocky soil. As recorded by the high-altitude Pyramid meteorological station (5,050 m a.s.l.) (http://evk2. isac.cnr.it/) in the Khumbu Valley, the average annual sum of precipitation was 343 mm from 2005 to 2008. The wettest month was July (103 mm); very little precipitation (13 mm) fell from December to April. Based on a lapse rate of 0.6 °C/100 m, the mean temperatures in the coldest Fig. 1 Landscape with C. fastigiata dwarf shrubs above the Juniperus saltuaria treeline (4,400 m a.s.l.) on the south-eastern Tibetan Plateau during midsummer; the sampling site is indicated by a vertical arrow (a). C. fastigiata growing in clusters (b) 123 Author's personal copy Trees (2015) 29:79–86 81 Fig. 2 Location of the study area in a larger context of the Tibetan Plateau (inset) and of the two study sites (yellow triangles) of C. fastigiata on the south-eastern Tibetan Plateau (site 1) and in the central Himalayas (close to Mt. Everest) (site 2) as well as of the nearby meteorological station in Nyingchi (3) (black square) and one grid dataset from CRU TS 3.0 at 0.5° spatial resolution (4) (black square) (January) and the warmest month (July) were calculated to be -3.2 and 10.1 °C at the sampling site, respectively. Precipitation in the form of snow is common except for the monsoon season. The main differences between sites 1 and 2 are the exposition, south facing vs. north facing, and the annual sum of precipitation, 957 vs. 343 mm. From each site, 20 shoots, as thick as possible, with diameters from 0.6 to 3.0 mm were sampled with a distance of 2–3 m in-between them to avoid sampling of the same genotype twice. Samples were collected in 2012 in the central Himalayas and in 2010 and 2012 on the southeastern Tibetan Plateau. 2010). For this purpose, cross-sections were taken every 2–3 cm along the shoots. The ring widths were measured based on digital images along two radii per cross-section under a reflected light microscope using the program ImageJ (Schneider et al. 2012) with a precision of 1 lm. After visual cross-dating, these two series of measurements were averaged to one series for each shoot. The correlation of each individual ring-width series with the site chronology (made from all individual ring-width series of a site except the candidate growth-ring series to be tested) was calculated using the COFECHA program (Holmes 1983); poorly correlating ring-width series (r \ 0.40) were eliminated from further analysis. Wood anatomy and cross-dating Data analysis A 5-mm long piece of each shoot was taken from close to soil level and embedded in paraffin. Then, 8–10 lm thick cross-sections were cut using a sledge microtome and stained with 3 % safranin (Merck, Darmstadt, Germany) for enhancing the contrast. The relevance of missing outer rings close to the soil level, occurring at various distributional margins of woody plant species, has recently been described by Wilmking et al. (2012). The presence of missing (outer) rings can be problematic for the establishment of shrub-ring chronologies, because of cross-dating difficulties. To get an impression from the growth variations along the shoots, three individuals from site 1 were examined using the so-called serial sectioning technique (Kolishchuk 1990; Ba¨r et al. 2007; Hallinger et al. The mean correlation among all shoots from a site (rbar) was calculated as a common measure for the similarity within a group of growth-ring series. The mean sensitivity, measuring the year-to-year variability within a ring-width series, was also calculated. The mean autocorrelation of a ring-width series measures how much the ring width in year n is correlated with the ring width in year n-1 (Fritts 1976). The two site chronologies assembled were correlated with monthly meteorological data for temperature and precipitation. For site 1, the meteorological data were obtained from the station in Nyingchi (3,000 m a.s.l.). For site 2, the data from one nearby grid point (27.75°N, 123 Author's personal copy 82 Trees (2015) 29:79–86 86.75°E) of the CRU TS 3.0 (Climatic Research Unit, Time Series Datasets, version 3.0) were used (Mitchell and Jones 2005). The CRU data correlate well with the local meteorological measurements (Liang et al. 2014). The similarity between the site chronologies and the significant, seasonalized climatic variables was described by the simple correlation coefficient (r), measuring the medium-term coherence, and the coefficient of coincidence (G) (‘Gleichla¨ufigkeit’) for the year-to-year agreement (Eckstein and Bauch 1969). Results and discussion four shoots were eliminated because of abnormal growth patterns of which the causes remained unknown. The synchronism of the variation in the ring-width series from different shoots suggested the influence of an external factor, very likely of climate, on the annual growth. The average correlation coefficient between the tree-ring series of the shoots was 0.68 at site 1 and 0.54 at site 2, thus confirming the reliability of cross-dating. The average firstorder autocorrelation of the individual ring-width series per site (calculated from the raw measurements) was low (0.09 and 0.16, respectively), thus making a trend elimination redundant. The mean sensitivity was 0.44 at both sites which is evidence for high year-to-year differences in ring widths. Cross-dating and chronology development Wood anatomy and age of C. fastigiata The outer growth rings throughout each C. fastigiata shoot were obviously formed at the same time, as shown by ring widths measured on seven cross-sections taken along one shoot (Fig. 3). The results obtained for the other two plants were identical. The same holds for rhododendron and juniper shrubs on the Tibetan Plateau (Liang and Eckstein 2009; Liang et al. 2012). Therefore, we concluded that cross-sections taken close to the soil level contain the maximum possible number of growth rings. Cross-dating between tree-ring series was facilitated by the occurrence of narrow (and missing) rings in 2000 and 2004 on the south-eastern Tibetan Plateau and in 2002, 2005 and 2008 in the central Himalayas (Fig. 6). Out of a total of 20 shoots per site, 19 and 10 shoots could be crossdated for site 1 and 2, respectively. Seven shoots were excluded because their tree-ring series correlated poorly with the site chronologies. Moreover, the tree-ring series of Annual ring width (μm) 100 80 ο 60 40 20 1998 2000 2002 2004 2006 2008 2010 Year Fig. 3 Ring-width series obtained from serial sectioning (seven cross-sections) from soil level up to the top of one shoot of C. fastigiata, sampled in 2010; accordingly, the uppermost cross-section contains only one growth ring marked by a small circle on the y-axis on the right-hand side 123 Cross-sections of C. fastigiata shoots show a diffuse-porous to semi ring-porous growth-ring structure leading to clear ring boundaries (Fig. 4). The latter is further highlighted by nearly vessel-free tissue consisting of thickwalled fibers. The ring widths ranged from 13 to 150 lm, and their average was 51.8 ± 19.8 lm at site 1 and 64.4 ± 25.7 lm at site 2. In some shoots, a few growth rings were completely missing but their position could be identified through cross-dating with ring series from different shoots. In the time series, missing rings were given a width of zero. The ring width of C. fastigiata is much narrower than of several alpine and arctic shrub species under cold environments, such as Empetrum hermaphroditum with ring widths from 70 to 110 lm, depending on topographical aspects (Ba¨r et al. 2007), and Juniperus nana with ring widths from 117 to 321 lm along an elevation gradient from 770 to 1,100 m a.s.l. (Hallinger et al. 2010), both in Scandinavia. The mean ring width of C. fastigiata is also narrower than those of Salix pulchra (210 lm) and Betula nana (110 lm) (Blok et al. 2011) in the north-eastern Siberian tundra. According to Larcher (1987), organisms in harsh environments are not designed to maximize their biomass, but to stabilize at least a minimum of life functions for their survival. Moreover, cell physiological processes and metabolic activities of plants have been found to be more resource demanding in extreme ecosystems than under temperate conditions (Lu¨tz et al. 2012), likely resulting in the extremely narrow growth rings of highelevation C. fastigiata. The C. fastigiata shoots reached an age of around 30 years. More fieldwork is needed to locate older populations. Based on the annual shoot elongation, C. tetragona in the High Arctic can reach a life span of more than 100 years (Rayback and Henry 2005; Rozema et al. 2009; Weijers et al. 2010, 2013; Rayback et al. 2012a). Genets of Author's personal copy Trees (2015) 29:79–86 83 Fig. 4 Cross-sections (a, b) from a shoot of C. fastigiata, showing clear annual growth rings; scale bar length 200 lm 0.6 0.6 (A) * * 0.4 0.4 0.2 0.2 0.0 0.0 Correlation coefficient pS pO pN pD J F M A M J J A pS -0.2 -0.2 -0.4 -0.4 -0.6 -0.6 0.6 pO pN pD 0.6 (B) * 0.4 0.4 0.2 0.2 0.0 J F M A M J J A * * * 0.0 pS pO pN pD J F M A M J J A pS -0.2 -0.2 -0.4 -0.4 -0.6 pO pN pD J F M A M J J A -0.6 pS pO pN pD J F M A M J J A Monthly mean maximum temperature Monthly mean minimum temperature Monthly mean temperature pS pO pN pD J F M A M J J A Month Monthly sum of precipitation Fig. 5 Correlation between the ring-width chronologies of C. fastigiata and various climatic variables from September of the previous year to August of the current year at site 1 (a) and site 2 (b); asterisk represents the significance at the p \ 0.05 level C. tetragona may live even up to several hundred years (Havstro¨m et al. 1993; Johnstone and Henry 1997). We deem it likely that C. fastigiata is able to reach similar ages. Climate/growth association The growth of C. fastigiata at both sites is positively associated with temperature in late winter/early spring 123 Author's personal copy 84 3 (A) 2 Chronology at Site 1 Mean monthly minimum temperature from Feb to Mar 20 15 1 10 0 -1 5 0 -3 1985 3 (B) 1990 1995 2000 2005 2010 Chronology at Site 2 Sum of precipitation in prior Sep-Dec 15 2 Sample depth -2 Z score Fig. 6 Graphical comparison between the two C. fastigiata site chronologies and seasonalized climate records. a at site 1, annual ring width is associated with February to March temperature (r = 0.54, p \ 0.01; G = 68 %, p = 0.5); b at site 2, annual ring width is associated with sum of precipitation from September to December in the previous autumn (r = 0.60, p \ 0.001; G = 88 %, p = 0.01). All variables were transformed to Z-scores to facilitate visual comparison. The dotted lines (smallest dots) indicate sample depth Trees (2015) 29:79–86 10 1 0 5 -1 -2 0 -3 1985 1990 1995 2000 2005 2010 Year (February–March) (Figs. 5, 6a). According to Ko¨rner (2003), winter temperatures are critical for the distribution of plant species. This holds also true for most tree species at high elevations, showing a strong positive association to temperature in late winter/early spring (e.g., Oberhuber 2004; Zhu et al. 2008; Liang et al. 2009). Low temperatures in late winter/early spring may damage the leaf buds of C. fastigiata and hence result in narrow rings. Its growth, however, does not show any significant association with summer temperature, unlike C. tetragona in the High Arctic (Rayback and Henry 2005; Weijers et al. 2010). Other than with temperature, radial growth of C. fastigiata at sites 1 and 2 responded differently to precipitation. At site 1, its growth did not correlate with precipitation, similar as Abies georgei var. smithii at humid timberlines (Liang et al. 2009) in the same area. At site 2, however, it showed significantly positive correlations with precipitation in the autumn prior to growth (September– December) (Figs. 5, 6b) and in the current spring (April– May). From September to December, precipitation falls as snow thus preventing frost damage and increasing soil moisture availability in the early growing season. April– May precipitation amounted to only 17 mm from 2005 to 2008, as recorded at the Pyramid station (5,050 m a.s.l.); our sampling site in the rain shadow may receive even less precipitation. This explains the correlation found with April–May precipitation at site 2. Such climate response is similar as of timberline Betula utilis in the central Himalayas whose growth is strongly limited by precipitation in spring (Liang et al. 2014). The same situation is valid for 123 high-elevation (up to 4,800 m a.s.l.) juniper shrubs on the central Tibetan Plateau (Liang et al. 2012). Conclusions C. fastigiata, in spite of its extremely slow growth, forms distinct annual growth rings, and the selected ring-width series cross-date well, indicating its dendroecological potential. Its annual radial growth reflects a temperature signal in late winter/early spring at both sites. Precipitation is the main growth-controlling factor in the central Himalayas, but not on the south-eastern Tibetan Plateau. In spite of its markedly different growth form as compared to trees, C. fastigiata partly captures the same year-to-year macroclimatic variations as nearby timberline trees. Author contribution statement Eryuan Liang: funding, experimental design, fieldwork, data analysis, development and writing of the manuscript, review and discussion of the manuscript. Wenwen Liu: processing samples and data analysis, review and discussion of the manuscript. Ping Ren: processing samples and data analysis, review and discussion of the manuscript. Binod Dawadi: fieldwork, review and discussion of the manuscript. Dieter Eckstein: data analysis, writing of the manuscript, review and discussion of the manuscript. Acknowledgments This work was supported by the National Natural Science Foundation of China (41471158, 41130529) and the National Basic Research Program of China (2012FY111400). We appreciate the great support from the Southeast Tibet Station for Alpine Environment, Observation and Research, Chinese Academy of Sciences. 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