Spatial structure of the regeneration of Scots pine under two silvicultural systems. F. Montes, M. Pardos and I. Cañellas 1 CIFOR-INIA. Ctra. de la Coruña km 7.5 28040 Madrid Spain e-mail: fmontes@inia.es _____________________________________________________________________ Abstract This paper is focused in the assessment of the effects of Silviculture on the structure of two even-aged Scots pine stands across a rotation period . For this purpose, 2 plots of 0.5 ha in different aged stands were established in two Scots pine forests with different management systems in the Central Mountain Range of Spain. To asses the spatial pattern the L(d) function were employed. To analyse the spatial relationship between the mother trees and the recruitment, a function derived from K(d) function was used. In Valsaín forest, the shelterwood fellings are carried out gradually over a irregular spaced stand, leading to a mixture of several cohorts and a cluster spatial pattern at 15-20 m for the stem distribution during the shelter phase. The regeneration showed repulsion from the old crop at very short distances and at distances greater to 15 m. In Navafría forest, the regular distribution of the trees and the short period used to regenerate the stand led to a positive spatial association between the mother trees and the seedlings at large scale. _____________________________________________________________________ Introduction The regeneration process is a key factor that determines the structure of the forest, and its knowledge is of great importance for sustainable forest management. Several approaches focussed on different scales and different stand features have been used to assess forest structure. The spatial pattern can be analysed using the Ripley’s K(d) function if mapped data are available at stand level (Moeur, 1993; Kuuluvainen, 1996; Aldrich, 2003), as well as the geostatistical tools at broader scales or when data are taken in sample points (Denslow, 2000). However, there are not suitable tools to analyse the spatial relationship between the stem pattern and the spatial distribution of seedlings or saplings, because of the different scale of both processes that require different sampling strategies (Goreaud & Pélissier, 2003). This paper is focused in the assessment of the effect of Silviculture and the stand structure on the regeneration process in two Scots pine forests that stand for the most commonly used management methods for the species in the Central Mountain range of Spain (Montes et al. 2005). For that purpose, a new function termed Krx(d), that allows to analyse the spatial relationship between a point process and a sampled variable, was derived from the intertype Krs(d) function for points belonging to two classes, to analyse the relationship between stems and seedlings or saplings during the regeneration process. Material and methods Study site Two 5000 m2 plots were installed, one at the beginning of the regeneration period, in a 81-100 years old stand, in Navafría, and the other in a 0-20 years old stand, in Valsaín accompanied by a residual crop of mother trees. In each plot, all the stems (trees with diameter at breast height (DBH) larger than 10 cm) were positioned through their xy coordinates, the saplings (higher than 1.30 m height and DBH less than 10 cm) were counted in 2x2 m2 quadrats throughout the plot and the seedlings were positioned in four 25 m2 subplots (divided in a hundred 0.25 m2 plots). L(d) function The spatial pattern of seedlings and stems was analysed using the Ripley’s K(d) function (Ripley, 1977). K(d) was calculated from the equation: λK (d ) = ∑ in=1 ∑ nj =1 δ ij (d ) n ⎡1 if d ij ≤ d ⎣0 if d ij > d δ ij (d ) ⎢ , i ≠ j, (1) where λ is the density of stems per unit area, dij the distance from tree i to tree j, and n the number of trees in a circular area of radius d. The K value is compared to 95% quantiles of a Poisson distribution obtained through 99 simulations of the Poisson process (Ripley, 1977). To deal with the boundary effect of the plot, δij(d) was replaced by ωij(d), which is 0 if stems i and j are more distant than d, and in other case gives the fraction contained within the plot of a circumference centred in i that falls over j. The transformation Lˆ (d ) , which linearizes the K function and stabilizes its variance, was used: Lˆ (d ) = Kˆ (d ) π −d (2) Spatial relationship between sapling density and stems spatial distribution: Krx(d) function In order to analyse the spatial relationship between a spatial point pattern (as is the stem distribution in the experimental plots) and a continuous spatial variable (as is the sapling or seedling density in quadrats) a modification of the K(d) function that allows to characterize the negative or positive spatial association between the point distribution and the variable values was developed (Eq. 3). K rx ⎛ N n ⎡ (x − x )⎤ n N ⎡ (x j − x )⎤ ⎞ ⎜ ∑∑ ω ij ( d ) ⋅ ⎢ j + ∑∑ ω ji ( d ) ⋅ ⎢ ⎥ ⎥ ⎟⎟ ⎜ i =1 j =1 s s x x ⎣ ⎦ j =1 j =1 ⎣ ⎦⎠ =⎝ N n n N ∑∑ ω rs (d ) + ∑∑ ω sr (d ) r =1 s =1 ∑ (x n s x2 = j =1 (3) s =1 r =1 − x) 2 j n (4) where N is the number of stems, n is the number of samples were the variable was measured, xj is the value of the variable in the sample j and ωij is calculated as described for the K(d) function. To set the boundaries of the 95% confidence interval of a independent distribution of the stems and the sapling density or the seedling density, a Montecarlo test was carried out, simulating 99 random distribution of stems and assigning each time randomly the measured values of the variable to the samples. Results Spatial pattern of stems In Navafría the mother trees, during the regeneration fellings, show a regular spatial pattern at shorter scales, till 8 m approximately. In Valsaín, the mother trees show a cluster pattern at scales between 8 and 20 m when the regeneration fellings start. At the end of the regeneration period, the cluster pattern of the young stems at shorter scales overlaps the cluster pattern at larger scales of the mother trees (Figure 1). Valsaín 1.50 1.00 1.00 0.50 0.50 L(d) L(d) Navafría 1.50 0.00 -0.50 0.00 -0.50 -1.00 -1.00 0 10 20 0 Distance (m) 10 20 Distance (m) Figure 1. Analysis through the L(d) function of the spatial pattern of the stems in the experimental plots of Navafría and Valsaín. Spatial relationship between seedlings and stems Figure 3 shows the Krx(d) function in the plots of Navafría and Valsaín, for the spatial arrangement of the mother trees and the seedling density in 4 randomly distributed plots of 25 m2 divided in 100 quadrats of 0.25 m2. In Navafría, seedlings show positive spatial relationship with mother trees at scales between 10 and 20 m. In Valsaín plot, the young strata form dense patches, giving a negative spatial relationship between stem density and seedling density at short distances and beyond 15 m. Valsaín 0.30 0.20 0.10 Krx(d) Krx(d) Navafría 0.25 0.2 0.15 0.1 0.05 0 -0.05 -0.1 -0.15 0.00 -0.10 -0.20 -0.30 0 10 Distance (m) 20 0 10 20 Distance (m) Figure 2. Analysis through the Krx(d) function of the spatial relationship between the stems and the seedling density in the experimental plot of Navafría, where regeneration fellings have just started, and in the experimental plot in Valsaín, at the end of the regeneration period. Spatial relationship between saplings and stems in the experimental plot of Valsaín Figure 3 shows the Krx(d) function, for the spatial arrangement of the sapling density in the 2×2 m2 quadrats in Valsaín’s plot. It can be seen the negative spatial association between saplings and the dense patches of young stems in all the analysed range. 1-20 years 0.10 Krx(d) 0.05 0.00 -0.05 -0.10 0 10 20 Distance (m) Figure 3. Analysis through the Krx(d) function of the spatial relationship between the stems and the sapling density in experimental plot of Valsaín. Discussion In this paper the Lrx(d) function is proposed to find the spatial relationship between the pattern of the stems and the structure of continuous variables such as sapling density. This function may have many applications in forest ecology research, because the trees form a point pattern associated with continuous variables, such as soil properties or slope, or to determine the spatial structure of other vegetation strata or fungus populations which are measured using density samples. The Lrx(d) function is independent of the sampling location where the spatial continuous variable is measured because it is divided by the sum of the terms ωij(d). The value of the Lrx(d) function depends only on the value of the variable and the local density of trees, eliminating the effect of the interaction between the location of the samples and the point pattern. The value of the function depends on the spatial association between high values for the variable and the local density of the point pattern. The variable standardization through the expression (x j −x sx ) in eq. 3 gives values close to 0 under the assumption of spatial independence between the variable and the point pattern. Silviculture play an important role in the establishment process. In Navafría, the old stand is felled completely in a 20 years period, keeping a homogeneous distribution of the mother trees throughout the regeneration area. The low density of the stand at the beginning of the regeneration period favours the establishment of a dense herb layer, that hinders the success of natural regeneration, and often soil labour is required. The competence of herb layer, as far as the lack of mother trees’ protection from hard climatic conditions, lead to the positive spatial relationship between mother trees and seedlings in Navafría. Similarly, after a geostatistical analysis of the spatial structure of regeneration and the radiation conditions determined by the upper strata, Denslow et al. (2000) concluded that the regeneration pattern is independent from the highest radiation conditions. For the germination and development of the seedlings to occur, the radiation level would need to be above a certain threshold, but other factors such as the substrate (Pardos et al., 2004) or grazing (Aldrich et al., 2003) determine the spatial pattern of the regeneration. As the negative spatial association that the Krs(d) function shows between stems and saplings at large scales indicates, low density is required for seedling performance. Once the seedlings are established, it is necessary to eliminate both the shade and the competition from mother trees to permit stand development. In Valsaín, the regeneration period often extends during 40 years, and the fellings lead to a mosaic of dense gaps and clear gaps. The resulting structure is formed by several cohorts originating by different regeneration events at the first life stages of the stand. Natural regeneration is favoured by the microclimatic conditions gradient that the heterogeneous structure provides. Acknowledgments The authors wish to thank to Javier Donés and Juan Carlos Martín their help and knowledge of the studied forest, and to Angel Bachiller and Enrique Garriga for their collaboration in the field work. This study has been supported by the projects AGL 2000-1545 and AGL 2004-07094-CO2.01/FOR References Aldrich, P. R., Parker, G. R., Ward, J. S. & Michler, C. H. (2003) Spatial dispersion of trees in an old-growth temperate hardwood forest over 60 years of succession. Forest Ecology and Management, 180: 475-491Dale, M. R. T. 1999. Spatial pattern analysis in plant ecology. Cambridge University Press, Cambridge. Denslow, J. S. & Guzman, S. (2000) Variation in stand structure, light and seedling abundance across a tropical moist forest chronosequence, Panama. Journal of Vegetation Science, 11: 201-212. Goreaud, F. & Pélissier, R. (2003) Avoiding misinterpretation of biotic inteactions with the intertype K12-function: population independence vs. random labelling hypothesis. Journal of Vegetation Science, 14: 681-692. Kuuluvainen, T., Penttinen, A., Leinonen, L. & Nygren, M. (1996) Statistical opportunities for comparing stand structural heterogeneity in managed and primeval forests: an example from boreal Spruce forest in Southern Finland. Silva Fennica, 315328. Moeur, M. 1993. Characterizing spatial patterns of trees using stem-mapped data. Forest Science, 39(4): 756-775. Montes, F., Sánchez, M., Río, M. d. & Cañellas, I. (2005) Using historic management records to characterize teh effects of management on the structural diversity of forests. Forest Ecology and Management, 207: 279-293. Pardos, M., Montes, F., Aranda, I. & Cañellas, I. (2004) Influence of environmental conditions on socts pine (Pinus sylvestris L.) germinant survival and diversity in central Spain. Series of Conference Proceedings 1, Zentrum Wald-Forst-Holz Weihenstephan, Kloster Seeon, Germany. Ripley, B. D. (1977) Modelling spatial patterns (with discussion). J. Royal Statistical Society, 172-212.