Aleksey Fedorkov

Vitality and height growth of two Larix species and provenances in a field trial located in north-west Russia

Fedorkov A. (2014). Vitality and height growth of two Larix species and provenances in a field trial located in north-west Russia. Silva Fennica vol. 48 no. 1 article id 1053. https://doi.org/10.14214/sf.1053

Highlights

• Differences in tree vitality among provenances were insignificant (p > 0.05) at an early age
• The provenance effect was significant (p < 0.05) for total height
• These findings were in agreement with those of Lukkarinen et al. (2010) using the same material at the same age for field trial located in Punkaharju (Finland).

Abstract

Vitality and height of Larix species and provenances originating from Russia were estimated in a 5-yr field trial performed in the Komi Republic (north-west Russia) using a fully randomized single-tree plot design with 7–8 blocks. Tree provenance had no significant (p > 0.05) effect on tree vitality, though for Larix sukazcewii originating from the European part of Russia, trees from the northern regions were more vital than those from southern regions. Provenance was a significant (p < 0.05) factor for height, where the average height of 136 cm varied considerably (168 cm for trees from Nizhnij Novgorod and 111 cm for trees from Ufa). There were no significant correlations when vitality and height were compared to geographic and climatic variables for the locations.

Keywords
tree height; provenance trial; Russian larch; tree condition

Received 21 November 2013 Accepted 17 February 2014 Published 20 February 2014

Views 61850

Available at https://doi.org/10.14214/sf.1053 | Download PDF

1 Introduction

Larch (Larix Miller) is an economically and ecologically important group of tree species which grow in the boreal forests of the northern hemisphere. Most larch forests in the world, considering both distribution area and wood stock, are in Eurasia (Schmidt 1995). Larch is fast-growing tree species producing high quality timber (Chubinski et al. 1990) suitable for outdoor construction, due to its high mechanical strength and decay resistance (Polubojarinov et al. 2000). In Finland, larch is considered equivalent to Scots pine with respect to decay resistance (Venäläinen et al. 2001). In general, larch forests in Russia cover more than 280 million hectares, accounting for 37% of the forested area and 30.7% of the wood stock (Martinsson and Lesinski 2007).

The nomenclature of the Eurasian larch species is complex and may vary by country (Eysteinsson and Skúlason 1995; Abaimov et al. 2002; Lukkarinen et al. 2009; Karlman 2010). According to Farjon (1990), two larch species are recognized in Russia, the Siberian larch (L. sibirica Ledeb.) and the Dahurian larch (L. gmelinii Rupr.). Dylis (1947) suggested that L. sukaczewii Dyl. is a separate species in the European part of Russia, but according to Bobrov (1978), L. sukaczewii cannot be distinguished from L. sibirica Ledeb. found in the central part of Siberia. Later phylogenetic studies (Bashalkhanov et al. 2003; Khatab et al. 2008; Neyton et al. 2008) confirmed that L. sukaczewii is a separate species. The series of the field trials with the same material of Russian larches was established in Canada, China, Finland, France, Iceland, Japan, Norway, Russia, Sweden and the United States (Martinsson and Takata 2005). Recently Lukkarinen et al. (2010) and Karlman et al. (2011) reported on survival, growth and damage to Russian larch material at the age four and five years in the field trials located in Finland and Sweden, respectively.

The objectives of this study were to compare vitality and growth of L. sukaczewii and L. sibirica seedlings under field conditions; evaluate the relationships between tree vitality and growth with climatic and geographic variables; and to study genotype × environment interaction for L. sukaczewii and L. sibirica at the provenance level using the findings of Lukkarinen et al. (2010) and Karlman et al. (2011). These results would be important for a proper selection of provenances for commercial planting.

2 Material and methods

2.1 Field trial and material

The study was performed in a field trial located near the town of Syktyvkar in the Komi Republic (NW Russia) (61°39´N, 50°41´E, alt. 160 m a.s.l) and seed collection accomplished as described in the Russian-Scandinavian Larch Project of 1994–2000 (Abaimov et al. 2002) (Table 1). Seeds were sown in containers (7×7 cells/container, cell size of 128 cm³) in May 2006 and grown in a plastic greenhouse without supplemental heat or light. At the beginning of August 2006, seedlings were moved to the open air before planting. The two-year-old seedlings were planted in September 2007, with a spacing of 3×1 m using a fully randomized single-tree plot design with 7–8 blocks (20–25 seedlings from each provenance). The 1068 seedlings were planted in a clear-cut area with sandy soil prepared using a plough.

2.2 Measurements

The height and vitality of all trees on the plantation were estimated after five growing seasons in the field (autumn 2012). Tree vitality was evaluated using the following classification scheme: 1 – healthy tree, shoots healthy, stem straight and growing vigorously; 2 – slightly damaged, good condition, shoots healthy, main stem straight; 3 – seriously damaged tree, poor condition, terminal shoot damaged, bent or dead, retarded growth; and 4 – dead tree. The height of living trees was measured in centimetres and the survival percentage was based upon the proportion of living trees at the time of the assessment.

2.3 Statistical analysis

Statistical analysis was performed on a plot mean basis as independent units. Although vitality was observed on a discontinuous scale, mean values calculated from the original class codes were continuous and normally distributed. The differences in survival, vitality and height between species (L. sukaczewii vs. L. sibirica) were analysed by T-test. Taking into account the complicated nomenclature of Eurasian larch species, statistical analysis was performed for all provenances together. The statistical significance of provenance and block effects on tree vitality and height were studied using ANOVA. The linear model equation was defined as:

where y_ijk = the vitality/height for plot means of the ith provenance in the jth block, μ = overall mean, P_i = the fixed effect of provenance, i = 1…6, B_j = the fixed effect of block, j = 1…8, and e_ij = the experimental error.

Differences between the highest mean and lower ones for provenances were analysed by Scheffe’s test and dependence between different parameters were tested with the Pearson correlation analysis. The Statistica 6.0 statistical package was used for all statistical analyses (SAS Institute Inc. 2004).

3 Results

The overall estimated survival in September 2012 was 82%, and varied between 78% and 86% according to provenance (Table 1). Differences between species were statistically insignificant (p > 0.05) for survival (T = –2.167; p = 0.096), vitality (T = 0.729; p = 0.470) and height (T = 0.713; p = 0.479). Provenance had no significant (p > 0.05) effect on tree vitality (Tables 2 and 3), though for L. sukazcewii from the European part of Russia, trees from the north were more vital than those from the south.

Provenance was a significant (p < 0.05) factor for height (Table 2). The average height was 136 cm, and varied according to provenance (168 cm for Nizhnij Novgorod and 111 cm for Ufa) (Table 3). The block effect was insignificant (p > 0.05) for tree vitality and growth (Table 2). There were no significant correlations when vitality and height were compared to geographic and climatic variables of the provenances. For vitality, there was a modest, but insignificant correlation with latitude and temperature sum (Table 4).

4 Discussion and conclusions

The results obtained by Lukkarinen et al. (2010) and Karlman et al. (2011) using similar materials (of approximately the same age) for field trials in Finland and Sweden offered an opportunity to compare larch tree vitality and growth along a longitudinal gradient. The field trials at Särna (61°31´N, 13°00´E) in Sweden and at Punkaharju (61°49´N, 29°19´E) in Finland were at similar latitudes (but a different longitude) to the Syktyvkar field trial (see Materials and methods). The longitudinal distances between Syktyvkar and the sites of the two other field trials, Särna and Punkaharju, were ~40º and 20º (approximately 2000 and 1000 km), respectively. The comparison between survival (vitality) and height (for similar materials) between these trials can provide information about the effects of longitude on these parameters.

The overall survival was higher (by about 20%) for the Syktyvkar field trial compared to the Särna and Punkaharju trials. The reason for the lower survival at Punkaharju was pine weevil damage to the seedlings (Lukkarinen et al. 2010), while Särna has very stony soil conditions, resulting in occasional poor soil scarification (Karlman et al. 2011). The higher altitude at Särna could also be an additional reason for increased seedling mortality. The difference between species survival was significant at the Särna (Sweden) site, but insignificant at Syktyvkar, where these differences between species at the Russian site could be explained by the low number of provenances investigated. Provenance had no effect on tree survival at Punkaharju and tree vitality at Syktyvkar, but this effect on survival was significant at Särna.

Results obtained by Rehfeldt et al. (2003) with respect to provenance for three larch species (L. sukaczewi, L .sibirica, and L. gmelinii) from throughout the former Soviet Union indicated that growth and survival of most populations are enhanced when populations are transferred to warmer climates. In both the Punkaharju and Syktyvkar field trials, trees from western and central Siberia had higher survival, while those from Särna had reduced survival which could be attributed to the higher altitude.

In general, tree growth was better in Punkaharju compared to the Syktyvkar and Särna sites, which was consistent with predictions made by Rehfeldt et al. (2003) indicating the temperature sum (1235 d.d.) was highest at Punkaharju. Among the provenances studied, the best growth at all three sites was seen for trees from Nizhnij Novgorod. The reduced growth for trees of southern origins (Perm and Ufa) seen in this study was attributed to the higher proportion of damaged trees having dead leader shoots and consequently, reduced height (Tables 1 and 3).

The overall findings from extensive provenance experiments within Scandinavia indicate that latitude has a significant effect on Scots pine hardiness and survival (Persson 1994; Persson and Ståhl 1990), a common pattern for general geographic variation of most forest tree species in the northern hemisphere (Wright 1976). The results obtained by Lukkarinen et al. (2010) at Punkaharju were similar to those of this study, but the correlation coefficient between survival and latitude was low (and insignificant) at Särna (Karlman et al. 2011). For tree height, the situation was reversed, where the correlation coefficient between height and latitude was low (and insignificant) at Punkaharju but highly significant at Särna. Although the correlation coefficient between tree vitality and latitude was insignificant in this study, there was a trend in greater vitality for trees of northern origin (Table 4). The non-significant correlation coefficients observed between the measured variables may be explained by the low number of the provenances investigated.

The results of this study, when taken together with data from trials in other geographic regions, can be used to compare vitality and height for different world climate regions, and may be able to provide information on the climatic adaptation of larch species and provenances. The suitability of larch species from different regions to be used in forest cultivation in NW Russia depends on population origin. However, the survival and growth of these populations must be followed for longer periods in field trials before any conclusions can be drawn about their utility to practical forestry.

Acknowledgements

I am grateful to Dr Owe Martinsson (Jämtland Institute for Rural Development, Sweden) for the larch seed lots provided, and the Helgeland Forest Society (Norway) for financial support. Many thanks go to the personnel of the Komi Republic Forestry Committee for seedling production and establishment of the field trial. I would like to acknowledge two anonymous reviewers for valuable comments and suggestions on the manuscript.

References

Abaimov A.P., Barzut V.M., Berkutenko A.N., Buitink J., Martinsson O., Milyutin L.I., Polezhaev A., Putenikhin V.P., Takata K. (2002). Seed collection and seed quality of Larix spp. from Russia, initial phase on the Russian-Scandinavian larch project. Eurasian Journal of Forest Research 4: 39–49.

Bashalkhanov S.I., Konstantinov Y.M., Vergitskii D.S., Kobzev V.F. (2003). Reconstruction of phylogenetic relationships of larch (Larix sukaczewii Dyl.) based on chloroplast DNA trnK intron sequences. Russian Journal of Genetics 39: 1322–1327. http://dx.doi.org/10.1023/A:1026166609055.

Bobrov E.G. (1978). [Standforming conifer species of USSR]. 189 p. [In Russian].

Chubinski A.N., Sosna L.M., Tsoy J.I. (1990). Siberian larch a good material for laminated veneer lumber production. Proc. International Timber Engineer Conference, Tokyo, Japan. p. 227–230.

Dylis N.W. (1947). [Siberian larch. Materials for taxonomy, geography and history]. Moscow Society of Naturalists, Мoscow. 137 p. [In Russian].

Farjon A. (1990). Pinaceae. Drawings and descriptions of the genera Abies, Cedrus, Pseudolarix, Keteleera, Nothotsuga, Tsuga, Cathaya, Pseudotsuga, Larix and Picea. Koelts Scientific Books, Königsten, Germany. 330 p.

Eysteinsson T., Skúlason B. (1995). Adaptation of Siberian and Russian larch provenances to spring frost and cold summers. Icelandic Agricultural Science 9: 91–97.

Karlman L. (2010). Genetic variation in frost tolerance, juvenile growth and timber production in Russian larches (Larix Mill.) – implications for use in Sweden. Doctoral thesis 2010:30. Faculty of Forest Science, Swedish University of Agricultural Sciences, Umeå. 64 p.

Karlman L., Fries A., Martinsson U., Westin J. (2011). Juvenile growth of provenances and open pollinated families of four Russian larch species (Larix Mill.) in Swedish field tests. Silvae Genetica 60: 165–177.

Khatab I.A., Ishiyama H., Inomata N., Wang X-R., Szmidt A.E. (2008). Phylogeography of Eurasian Larix species inferred from nucleotide variation in two nuclear genes. Genes and Genetic Systems 83: 55–66. http://dx.doi.org/10.1266/ggs.83.55.

Lukkarinen A.J., Ruotsalainen S., Nikkanen T., Peltola H. (2009). The growth rhythm and height growth of seedlings of Siberian (Larix sibirica Ledeb.) and Dahurian (Larix gmelinii Rupr.) larch provenances in greenhouse conditions. Silva Fennica 43: 5–20.

Lukkarinen A.J., Ruotsalainen S., Nikkanen T., Peltola H. (2010). Survival, height growth and damages of Siberian (Larix sibirica Ledeb.) and Dahurian (Larix gmelinii Rupr.) larch provenances in field trials located in southern and northern Finland. Silva Fennica 44: 727–747.

Martinsson O., Lesinski J. (2007). Siberian larch forestry and timber in a Scandinavian perspective. JiLU Jämtlands County Council Institute of Rural Development. Prinfo Accidenstryckeriet. 92 p.

Martinsson O., Takata K. (2005). International family test of Eurasian larch species. Eurasian Journal of Forest Research 8: 97–103.

Neyton H.T., Khatab I.A., Hemamali K.K., Inomata N., Wang X-R., Szmidt A. (2008). Phylogeography of Larix sukaczewii Dyl. and Larix sibirica L. inferred from nucleotide variation of nuclear genes. Tree genetics and genomics 4: 611–623.

Persson B. (1994). Effects of provenance transfer on survival in nine experimental series with Scots pine (Pinus sylvestris L.). Scandinavian Journal of Forest Research 9: 275–287. http://dx.doi.org/10.1080/02827589409382841.

Persson B., Ståhl E. (1990). Survival and yield of Pinus sylvestris L. as related to provenance transfer and spacing at high altitudes in northern Sweden. Scandinavian Journal of Forest Research 5: 381–395. http://dx.doi.org/10.1080/02827589009382621.

Polubojarinov O.I., Chubinski A.N., Martinsson O. (2000). Decay resistance of Siberian larch wood. Ambio 29(6): 352–353.

Rehfeldt G.E., Tchebakova N.M., Milyutin L.I., Parfenova E.I., Wykoff W.R., Kouzmina N.A. (2003). Assesing population responses to climate in Pinus sylvestris and Larix spp. of Eurasia with climate-transfer models. Eurasian Journal of Forest Research 6–2: 83–98.

SAS Institute Inc. (2004).SAS/STAT 9.1 user’s guide. SAS Publishing, Cary, NC.

Schmidt W.C. (1995). Around the world with Larix: an introduction. In: Schmidt W.C., McDonald K.J. (eds.). Ecology and management of Larix forests: a look ahead. USDA Forest Service, Intermountain Research Station, Technical Report GTR-INT 319.

Venäläinen M., Harju A.M., Nikkanen T., Paajanen L., Velling P., Viitanen H. (2001). Genetic variation in the decay resistance of Siberian larch (Larix sibirica Ledeb.) wood. Holzforschung 55: 1–6. http://dx.doi.org/10.1515/HF.2001.001.

Wright J.W. (1976). Introduction to forest genetics. Academic Press. 463 p.

Total of 23 references