Non-spatial and spatial analyses were carried out to study the effects on genetic parameters in ten-year height growth data across two series of 10 large second-generation full-sib progeny trials of western hemlock [Tsuga heterophylla (Raf.) Sarg.] in British Columbia. To account for different and complex patterns of environmental heterogeneity, spatial single trial analyses were conducted using an individual-tree mixed model with a two-dimensional smoothing surface with tensor product of B-spline bases. The spatial single trial analysis, in all cases, showed sizeable lower Deviance Information Criterion values relative to the non-spatial analysis. Also, fitting a surface displayed a consistent reduction in the posterior mean as well as a decrease in the standard deviations of error variance, no appreciable changes in the additive variance, an increase of individual narrow-sense heritability, and accuracy of breeding values. The tensor product of cubic basis functions of B-spline based on a mixed model framework does provide a useful new alternative to model different and complex patterns of spatial variability within sites in forest genetic trials. Individual narrow-sense heritabilities estimates from the spatial single trial analyses were low (average of 0.06), but typical of this species. Estimated dominance relative to additive variances were unstable across sites (from 0.00 to 1.59). The implications of these estimations will be discussed with respect to the western hemlock genetic improvement program in British Columbia.
The aim of the study was to compare the densities of red squirrel (Sciurus vulgaris) in the arboretum and a neighbouring forest and to investigate which tree species the squirrels used. The study was conducted in the area of the Rogów Arboretum (53.76 ha) and the so-called Zimna Woda and Wilczy Dół forest complexes (altogether 536 ha), all being part of an Experimental Forest Station in Rogów. The density of squirrels in the arboretum and the neighbouring forest was estimated and compared by means of snow tracks on transect routes. Changes in the abundance of squirrels throughout one year as well as their behaviour were determined on the basis of direct observations along transects running through the arboretum. More than half of the area of the arboretum was searched in order to record feeding signs of squirrels. Additionally, trees with bark stripping were recorded.
The density of snow tracks was higher in the arboretum (0.19 tracks/100 m/24 h) than in the neighbouring forest (0.09 tracks/100 m/24 h). The largest number of observations of red squirrels along transects was made between February and April, in July and August and in October and November. In about half of the cases, squirrels were feeding on one of six non-native tree species (most often on cones of Macedonian pine, Pinus peuce). Feeding signs were found on 39 plots (17%) and 16 different tree species. The most numerous feeding signs were found on plots with Douglas fir (Pseudotsuga menziesii) and also on plots with the western hemlock (Tsuga heterophylla), Swiss pine (Pinus cembra), mountain silverbell (Halesia monticola) as well as shagbark (Carya ovata) and shellbark hickories (C. laciniosa). On eight plots, trees with signs of bark stripping were found, most commonly on Sawara cypress (Chamaecyparis pisifera). Its soft bark was probably used to build dreys. In the area of the arboretum, the natural food sources (seeds of native trees) are supplemented with numerous non-native tree species, which seeds are also consumed by squirrels. The highly abundant and diverse food sources promote a higher density of the red squirrel in the area of the arboretum. Additionally, when tree seeds are scarce in the neighbouring forest, squirrels migrate into the arboretum.
production of Miscanthus sinensis ‘Tatai’ in the condition of South-Western Slovakia. In Acta Regionalia et Environmetalica, vol. 10, 2013, no. 2, pp. 55–58. DOI: 10.2478/aree-2013-0012. RICHARDSON, A.D. – ASHTON, P.M.S. – BERLYN, G.P – Mc GRODY, M.E. – CAMERON, I.R. 2001. Within-crown foliar plasticity of western hemlock, Tsugaheterophylla in relation to stand age. In Annals of Botany, vol. 88, 2001, pp. 1007–1015. RAYBURN, A.L. – Crawford, J. – RAYBURN, CH.M. – JUVIK, J.A. 2009. Genome size of three Miscanthus species. In Plant Molecular Biology Reporter, Springer
materii organicznej gleb [Methodical guide-book for soil organic matter studies]. Prace Komisji Naukowych Polskiego Towarzystwa Gleboznawczego, N. 120, Komisja chemii gleb, Zespół Materii Organicznej Gleb, N II/16, 65 p. FECENKO, J. – MALIŠ, Ľ. – KOVÁČIK, P. 1995. Effects of sodium humate on the yield formation and quality of spring barley. In Zeszyty Problemowe Postepów Nauk rolniczych , vol. 421 , pp. 31‒36. GILL, R.S. – LAVENDER, D.P. 1983. Urea fertilization and foliar nutrient composition of western hemlock ( Tsugaheterophylla (Raf.) Sarc.). In Forest Ecology
Products Society (1994), 13-16. Keithley. [WWW document]. - URL http://www.keithley.com [Accessed 20 October 2013]. Lazarescu, C., Avramidis, S., Oliveira, L. 2010. Shrinkage response to tensile stress during hemlock (Tsugaheterophylla) drying. - Proceedings of the 11th International IUFRO Wood Drying Conference, January 18-22, 2010, Skellefteå, Sweden, 122-130. Mettler-Toledo. [WWW document]. - URL http://www.mt.com [Accessed 20 October 2013]. Norberg, P. 1999. Monitoring wood moisture content using the WETCORR method. -Holz als Roh- und Werkstoff, 57, 448-453. Onysko
cabbage plants. In Journal of Environmental Management, vol. 200, pp. 243-252. GILL, R.S. - LAVENDER, D.P. 1983. Urea fertilization and foliar nutrient composition of western hemlock (Tsugaheterophylla (Raf.) Sarc.). In Forest Ecology and Management, vol. 6, no. 4, pp. 333-341. GUTIÉRREZ-MICELI, F.A. - SANTIAGO-BORRAZ, J. - MONTES MOLINA, J.A. - NAFATE, C.C. - ABUD-ARCHILA, M. - OLIVA LLAVEN, M.A. - RINCON-ROSALES, R. - DENDOOVEN L. 2007. Vermicompost as a soil supplement to improve growth, yield and fruit quality of tomato (Lycopersicum esculentum). In Bioresource
dynamics in old-growth Tsugaheterophylla/Thuja plicata forests. Forest Ecology and Management , 94: 175-186. Mugglestone A. M., Renshaw E. (1996). A practical quide to the spectral analysis of spatial point processes. Computational Statistics&Data Analysis , 21: 41-65. Payandeh B. 1974. Spatial pattern of trees in the major forest types of northern Ontario. Canadian Journal of Forest Research , 4: 8-14. Peterson Ch., Squiers E. 1995. An unexpected change in spatial pattern across 10 years in aspen-white pine forest. Journal of Ecology , 83: 847-855. Pielou E. C
Journal of Forest Research 36(11): 2920-2931. IVKOVIĆ, M., H. X. WU, T. A. MCRAE and C. A. MATHESON(2006b): Developing Breeding Objective for Pinus Radiata Pine Structural Wood Production II: Sensitivity Analyses. Canadian Journal of Forest Research 36(11): 2932-2942. IVKOVICH, M. and P. M. KOSHY (2002): Optimisation of multiple trait selection in western hemlock (Tsugaheterophylla [Raf.] Sarg.) including pulp and paper properties. Annals of Forest Science 59(5/6): 577-582. JAMES, R. N. (2001): Defining the product: Log grades used in Australia. RIRDC Publication No 01
-72. Pianka, E. R. 1966. Convexity, desert lizards, and spatial heterogeneity. - Ecology 47: 1055-1059. Pitkänen, S. 1997. Correlation between stand structure and ground vegetation: an analytical approach. - Plant Ecol. 131: 109-126. Pitkänen, S. 2000. Classification of vegetational diversity in managed boreal forests in eastern Finland. - Plant Ecol. 146: 11-28. Rambo, T.R. & Muir, P.S. 1998. Forest Floor Bryophytes of Pseudotsuga menziesii-Tsugaheterophylla Stands in Oregon: Influences of Substrate and Overstory. - Bryologist 101: 116-130. Ren, H. B., Niu, S. K., Zhang