Āris Jansons, Roberts Matisons (email), Oskars Krišāns, Baiba Džeriņa, Mārtiņš Zeps

Effect of initial fertilization on 34-year increment and wood properties of Norway spruce in Latvia

Jansons Ā., Matisons R., Krišāns O., Džeriņa B., Zeps M. (2016). Effect of initial fertilization on 34-year increment and wood properties of Norway spruce in Latvia. Silva Fennica vol. 50 no. 1 article id 1346. https://doi.org/10.14214/sf.1346

Highlights

  • The initial fertilization increased the productivity of Picea abies increasing stem volume by 17% at the age of 34 years
  • The tree-ring width was affected for up to15 years
  • The fertilization did not affect mean tree-ring density, although the latewood density was increased.

Abstract

Initial fertilisation, when the fertilizer is supplied during the plantation, is applied to improve the competitive ability of the seedlings and hence to increase their growth and productivity; however, fertilization could also alter wood properties and timber quality. In this study, the dimensions and tree-ring parameters – width, proportion of latewood, maximum and mean density, mean earlywood and latewood density – of initially fertilized (by 14, 6 and 11 g of N, P and K per seedling, respectively) Norway spruce (Picea abies Karst.) growing in an experimental plantation in Kalsnava, Latvia (temperate climate region) were assessed. The fertilization significantly increased the dimensions of trees in long-term (ca. 17% increase of stemwood volume). The analysis of tree-ring width suggested that the duration of the effect was ca. 15 years. The maximum and latewood density were higher for the fertilized trees only in a few years. The mean and earlywood density of tree-rings were mainly similar for both treatments. Altogether, considering the one-time application of a limited amount of fertilizer, such treatment had notable and lasting effect on Norway spruce.

Keywords
tree-rings; wood density; proportion of latewood; high-frequency densitometry; legacy effect; Picea abies

Author Info
  • Jansons, LSRFI “Silava”, Rigas str. 111, Salaspils, Latvia, LV2169 ORCID ID:E-mail aris.jansons@silava.lv
  • Matisons, LSRFI “Silava”, Rigas str. 111, Salaspils, Latvia, LV2169 ORCID ID:E-mail robism@inbox.lv (email)
  • Krišāns, LSRFI “Silava”, Rigas str. 111, Salaspils, Latvia, LV2169 ORCID ID:E-mail oskars.krisans@silava.lv
  • Džeriņa, LSRFI “Silava”, Rigas str. 111, Salaspils, Latvia, LV2169 ORCID ID:E-mail baiba.dzerina@silava.lv
  • Zeps, LSRFI “Silava”, Rigas str. 111, Salaspils, Latvia, LV2169 ORCID ID:E-mail martins.zeps@silava.lv

Received 31 March 2015 Accepted 13 November 2015 Published 24 November 2015

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Supplementary Files
1_Series_checking[PDF]
2_Basic_statistics[PDF]

1 Introduction

Fertilization is one of the most effective means of increasing the productivity of stands, especially for the nutrient-demanding species (Nohrstedt 2001; Saarsalmi and Mälkönen 2001; Sicard et al. 2006). However, fertilization also alters wood properties such as cell wall thickness, affecting wood density and hence the quality of timber (Mäkinen et al. 2002; Lundgren 2004; Cao et al. 2008). The gain from the fertilization might depend on the timing and manner of its application, as the positive effect might be diminished by e.g. competition (Nohrstedt 2001) or leakage (Ingerslev 1997). Still, the positive effect of fertilization of young Norway spruce (Picea abies Karst.) has been shown to persist up to eight years (Tamm 1965). The initial fertilization, when a limited amount of fertilizer is applied locally, before or during the plantation, has been used to boost the early growth of seedlings/saplings of spruce and hence to improve their competitive ability (Sicard et al. 2006), which strongly affects further development of a stand (Sutton 1995; Hytönen and Jylhä 2008). However, a rather small effect of such management on the increment has been reported (Sutton 1995). The effect of the initial fertilization on tree-ring properties and hence the physical strength and/or conductive properties of wood has been studied poorly. The aim of this study was to evaluate the effect of the initial fertilization on growth and tree-ring properties of Norway spruce in Latvia. We hypothesised that fertilization had a lasting effect on tree-ring properties.

2 Materials and methods

The study was carried out in the eastern part of Latvia (56°42´N, 25°57´E). The topography of the site was flat with elevation ca. 110 m a.s.l.; soil was loamy. Climate is mild, the mean annual temperature is ca. +6 °C; the monthly mean temperature ranges from –6.4 to +17.1 °C in January and July, respectively. The growing season extends for ca. 180 days. The annual sum of precipitation is ca.700 mm; approximately half of it falls during the June–September period.

The experimental plantation of Norway spruce was established in 1982 in Hylocomiosa forest type (Bušs 1976), planting 4-year-old bare-rooted saplings from a local provenance, enclosed in pressed peat capsules “Brika” (Rubtsow 1979), in prepared soil with the density of 4000 trees per ha, in four blocks by 200 trees within each. Directly after the planting, each sapling received ring fertilization at 10 cm distance, 14, 6 and 11 g of N (NH4NO3), P (superphosphate) and K (KNO3) per sapling (equalling 56, 24 and 44 kg ha-1), respectively. The treatment was applied for the entire blocks. Chemical weed control, by sprinkling simazine (3 kg ha-1) solution around the saplings, was applied twice during the first year.

In October 2013, a 5-mm increment core at the breast height was collected from 30 fertilized and 30 control undamaged dominant trees. In the laboratory, the increment cores were processed using the LignoStation wood analysis system (RinnTECH Inc., Heidelberg, Germany). A high-resolution (50 microns) wood density profile was acquired for each core using high-frequency probe (Schinker et al. 2003). For each tree-ring, 1) width, 2) latewood width, 3) mean density, density of 4) earlywood and 5) latewood and 6) maximum density was measured. The part of the tree-ring with density > 50% of the maximum density was considered as latewood. Additionally, data on height and diameter at 1.3 m height of 586 fertilized and 592 control trees were obtained from the inventory conducted in February 2012.

Considering that the outermost tree-ring(s) were sometimes lost during the sampling, the measured time series were crossdated and their quality was verified by a graphical inspection and statistically using the program COFECHA (Grissino-Mayer 2001), based on the tree-ring width. The time series, which had inconsistent dating, i.e. a match with the rest of the series both with and without a certain lag, were not used to avoid errors (Supplementary file 1). The time series of the measured tree-ring parameters of 24 fertilized and 24 control trees were crossdated consistently and passed the quality check. The comparison of tree-ring parameters of the analysed and the rejected trees is shown in Supplementary file 2. The proportion of latewood width (latewood width/tree-ring width) was calculated to describe the composition of tree-rings. The similarity of mean time series of the fertilized and control trees was described by Pearson correlation and Gleichläufigkeit (GLK) coefficients (Speer 2010). The tree-ring parameters for each year, mean time series of parameters and dimensions between the fertilized and control trees were compared by a t-test.

3 Results

The initial fertilization resulted in significantly (p-value < 0.01) higher dimensions (by ca. 3% and 7% and 17% for height, diameter and volume of stem, respectively) of spruce at the age of 34 years (Fig. 1). Statistics of the crossdated time series of the tree-ring parameters are shown in Table 1. The fertilization affected wood properties of Norway spruce as shown by the significant differences in mean values of some tree-ring parameters between the fertilized and control trees. The maximum and latewood density was significantly higher and the mean proportion of latewood was significantly lower for the fertilized trees (Table 1). The annual variation amongst the tree-ring parameters differed notably, but it was similar for the fertilized and control trees, and the mean time series calculated for them were rather synchronous (GLK > 0.55) (Table 2). The strength of the correlation between mean time series differed for the parameters (Table 2), it was weaker for the maximum and latewood density (0.40 and 0.53, respectively), suggesting that fertilisation has affected their patterns of annual variation.

1

Fig. 1. Height (A) and diameter at breast height (DBH) (B) of fertilized and control Norway spruce in winter of 2012 at the age of 34 years. Line shows median, box represents 1st and 3rd quartile, whiskers mark range (not exceeding 150% of interquartile distance) and circles denote outliers of the datasets.

Table 1. Statistics of tree-ring parameters (minimum (MIN), maximum (MAX) and mean (MEAN) values and their standard deviation (SD) and coefficient of variation (VAR)) of crossdated datasets and p-values of differences (DIFF) in mean values of mean time series of tree-ring parameters of fertilized and control Norway spruce in Kalsnava, Latvia.
  MIN MAX MEAN SD VAR DIFF
Maximum density, kg m–3
   Fertilized 258 1087 832 128 0.15  
   Control 376 1061 811 116 0.14 < 0.01
Mean density, kg m–3
   Fertilized 170 713 489 82 0.17  
   Control 144 760 495 86 0.17 0.69
Mean earlywood density, kg m–3
   Fertilized 84 638 400 86 0.22  
   Control 39 649 399 96 0.24 0.42
Mean latewood density, kg m–3
   Fertilized 229 931 692 113 0.16  
   Control 276 881 672 108 0.16 < 0.01
Tree-ring width, mm
   Fertilized 0.59 9.20 3.54 1.65 0.47
   Control 0.37 9.85 3.37 1.54 0.46 0.65
Proportion of latewood
   Fertilized 0.06 0.88 0.32 0.15 0.49  
   Control 0.05 0.94 0.37 0.16 0.45 < 0.01
Table 2. Pearson correlation (r) and Gleichläufigkeit (GLK) coefficients calculated between mean time series of crossdated datasets of tree-ring parameter of fertilized and control Norway spruce in Kalsnava, Latvia for 1987–2013.
  r GLK
Maximum density 0.40 0.77
Mean density 0.70 0.81
Earlywood density 0.66 0.69
Latewood density 0.53 0.55
Tree-ring width 0.88 0.81
Proportion of latewood 0.80 0.58

When the tree-ring parameters of fertilized and control trees were compared on the annual bases, most of the significant differences occurred in the first part of the analysed period (Fig. 2). In the beginning of the analysed period, tree-ring width was higher for the control trees for three years, but then it became significantly higher for the fertilized trees for the next eight consecutive years (up to 1998). Thus fertilization resulted in an additional 0.003 m2 of basal area (ca. 14%) per tree at the age of 34 years. In contrast, the proportion of latewood was higher for the control trees during most of the analysed period, but the differences were significant only in 1989, 1994–1997 and in 2001 (age 10–20 years). Maximum and latewood density was higher for fertilized trees during the first 12 years of the analysed period (until 1998), but the differences were significant only in a few years (1989, 1991 and 1994 or 1995). Such differences suggested that the effect of the initial fertilization lasted for ca. 15 years. Mean tree-ring density was similar for the fertilized and control trees during most of the analysed period; however, this parameter was significantly higher for the control trees in 2004 and 2006. Earlywood density was the only tree parameter, which showed no significant differences between the treatments (Fig. 2 E).

2

Fig. 2. Mean measurement (tree-ring width (A); proportion of latewood in tree-ring (B); maximum (C) and mean (D) wood density of tree-ring; earlywood (E) and latewood (F) density) time series and sample depth (G) of fertilized (black line) and control (grey line) Norway spruce. Asterisks indicate significance (p-value < 0.05) of differences between fertilized and control trees.

4 Discussion

The local application of initial NPK fertilization on saplings increased the dimensions of Norway spruce at the age of 34 years (Fig. 1), suggesting lasting effect of such treatment as previously observed in Central Europe (Sicard et al. 2006). The duration of the effect was evidenced by the significant differences in tree-ring width, proportion of latewood and maximum density for up to 15 years (Fig. 2 A, B). Generally, the fertilisation efficiently boosted early growth of the saplings, likely relieving them from the competition during the next years (Nilsson and Örlander 1999; Hytönen and Jylhä 2008). The reaction of Norway spruce to local fertilization (Fig. 1) was similar to that when the entire area of stand has been evenly fertilized (Nohrstedt 2001; Saarsalmi and Mälkönen 2001; Cao et al. 2008), although less nutrients were added per ha. Still, an inverse reaction to fertilization of radial increment was observed in the very beginning of the analysed period (Fig. 2 A). This might be explained by a slight over dosage of fertilizer, burdening early growth (Nohrstedt 2001; Saarsalmi and Mälkönen 2001), which, apparently, decreased after ca. 8 years, releasing the increment. Alternatively, this might be related to the differences in patterns of carbon allocation in the fertilized saplings (Alexsson and Alexsson 1986).

The differences in other tree-ring parameters during the first half of the analysed period were more consistent (Fig. 2). The fertilization decreased the proportion of latewood (Fig. 2 B) as previously observed by Mäkinen et al. (2002), likely decreasing the hardiness of heartwood (Zhang 1995). The fertilization also increased the maximum and latewood density (Fig. 2 C, F) that might be related to the differences in carbon allocation (Alexsson and Alexsson 1986). Nevertheless, this did not alter the mean tree-ring density (Fig. 2 D) as the contribution of the increased latewood density was likely countervailed by the higher proportion of the low-density earlywood. The earlywood is formed by thin-wall conducting cells; thus, its density was altered negligibly. The mean density of the fertilized trees was significantly lower compared to the control in 2004 and 2006 (Fig. 2 D) that might be related to higher environmental sensitivity of the faster growing trees (Martin-Benito et al. 2008).

5 Conclusions

The locally applied initial NPK fertilization increased the dimensions of Norway spruce at the age of 34 years and affected wood properties. The duration of the effect was ca. 15 years, likely due to the advances provided by higher rates of early growth. Nevertheless, the effect of fertilization was dual. Although fertilization improved the yields, it also increased the proportion of the softer earlywood. Hence, fertilisation did not affect mean tree-ring density; however, formation of a wider earlywood and denser latewood increased heterogeneity of wood.

Acknowledgements

Study was supported by European Social Fund project “Management of vital Norway spruce stands: ecological and technological aspects” (No. 2013/0022/1DP/1.1.1.2.0/13/APIA/VIAA/052). We also acknowledge Faculty of Biology of University of Latvia and Didzis Elferts, who provided access to the wood analysis system (acquired by ERAF project 2012/0001/2DP/2.1.1.3.1/11/IPIA/ VIAA/005). Andis Adamovičs helped during the collection of the material.

References

Alexsson E., Alexsson B. (1986). Changes in carbon allocation patterns in spruce and pine trees following irrigation and fertilization. Tree Physiology 2: 189–204. http://dx.doi.org/10.1093/treephys/2.1-2-3.189.

Bušs K. (1976). Latvijas PSR meža klasifikācijas pamati. [Basis of Forest Classification in SSR of Latvia]. LRZTIPI, Riga. 24 p. [In Latvian].

Cao T., Valsta L., Härkönen S., Saranpää P., Mäkelä A. (2008). Effects of thinning and fertilization on wood properties and economic returns for Norway spruce. Forest Ecology and Management 256: 1280–1289. http://dx.doi.org/10.1016/j.foreco.2008.06.025.

Grissino-Mayer H.D. (2001). Evaluating crossdating accuracy: a manual and tutorial for the computer program COFECHA. Tree-Ring Research 57: 205–221.

Hytönen J., Jylhä P. (2008). Fifteen-year response of weed control intensity and seedling type on Norway spruce survival and growth on arable land. Silva Fennica 42(3): 355–368. http://dx.doi.org/10.14214/sf.242.

Ingerslev M. (1997). Effects of liming and fertilization on growth, soil chemistry and soil water chemistry in a Norway spruce plantation on a nutrient-poor soil in Denmark. Forest ecology and Management 92: 55–66. http://dx.doi.org/10.1016/S0378-1127(96)03964-3.

Lundgren C. (2004). Cell wall thickness and tangential and radial cell diameter of fertilized and irrigated Norway spruce. Silva Fennica 38(1): 95–106. http://dx.doi.org/10.14214/sf.438.

Mäkinen H., Saranpää P., Linder S. (2002). Wood-density variation of Norway spruce in relation to nutrient optimization and fibre dimensions. Canadian Journal of Forest Research 32: 185–194. http://dx.doi.org/10.1139/x01-186.

Martin-Benito D., Cherubini P., del Rio M., Canellas I. (2008). Growth response to climate and drought in Pinus nigra Arn. trees of different crown classes. Trees 22: 363–373. http://dx.doi.org/10.1007/s00468-007-0191-6.

Nilsson U., Örlander G. (1999). Vegetation management on grass-dominated clearcuts planted with Norway spruce in southern Sweden. Canadian Journal of Forest Research 29: 1015–1026. http://dx.doi.org/10.1139/x99-071.

Nohrstedt H.O. (2001). Response of coniferous forest ecosystems on mineral soils to nutrient additions: a review of Swedish experiences. Scandinavian Journal of Forest Research 16: 555–573. http://dx.doi.org/10.1080/02827580152699385.

Rubtsow V.G. (ed.) (1979). Производство посадочного материала “Брикет”. [Production of planting material „Brika”]. ЛНИИЛН, Ленинград. 56 p [In Russian].

Saarsalmi A., Mälkönen E. (2001). Forest fertilization research in Finland: a literature review. Scandinavian Journal of Forest Research 16: 514–535. http://dx.doi.org/10.1080/02827580152699358.

Schinker M.G., Hansen N., Spiecker H. (2003). High-frequency densitometry – a new method for the rapid evaluation of wood density variations. IAWA Journal 24: 231–239. http://dx.doi.org/10.1163/22941932-90001592.

Sicard C., Saint-Andre L., Gelhaye D., Ragner J. (2006). Effect of initial fertilization on biomass and nutrient content of Norway spruce and Douglas-fir plantations at the same site. Trees 20: 229–246. http://dx.doi.org/10.1007/s00468-005-0030-6.

Speer J.H. (2010). Fundamentals of tree-ring research. The University of Arizona Press, Tucson. 333 p.

Sutton R.F. (1995). White spruce establishment: initial fertilization, weed control, and irrigation evaluated after three decades. New Forests 9: 123–133. http://dx.doi.org/10.1007/BF00028685.

Tamm O.C. (1965). Some experiences from forest fertilization trial in Sweden. Silva Fennica 117(3): 1–35. http://doi.org/10.14214/sf.a14283.

Zhang S.Y. (1995). Effect of growth rate on wood specific gravity and selected mechanical properties in individual species from distinct wood categories. Wood Science and Technology 29: 451–465. http://dx.doi.org/10.1007/BF00194204.

Total of 19 references.


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