Silvicultural opera ons increasingly aim to achieve desired water-related ecological services of forests and forest soils. Therefore, the eff ects of forest stand density, site, and soil depth on the water fl ow types were studied by conduc ng dye tracer experiments in two montane beech (Fagus sylva ca L.) forests located in the Western Carpathian Volcanic Range, Central Slovakia. Prevalent fl ow types were iden fi ed under usual weather condions. Brilliant Blue FCF dye tracer was periodically applied in powder form on 1-m 2 plots in forest stands with natural and reduced stand densi es, as well as in clear-cuts. When cumula ve precipita on reached approximately 100 mm, soil pits were excavated. The dye pa erns on the exposed profi les were photographed, and dye coverage, rela ve dye concentra on, and stain widths were determined at various soil depths using image analysis. These pa erns were used to discriminate two fl ow types. Con nuous ver cal dye plumes were interpreted as an indicator of surface-controlled fl ow type, which includes heterogeneous infi ltra on and macropore fl ow. The matrix-controlled fl ow type includes both homogeneous and heterogeneous matrix fl ow, as well as fi ngering. The log-linear analysis revealed that forest stand density and soil depth were signifi cantly related to the soil water fl ow type. Preferen al fl ow resulted from heterogeneous infi ltra on and fi ngering in the clear-cuts, from heterogeneous infi ltra on in the natural stands, and from macropore fl ow in the shelterwood stands. Dis nct humus forms and skeleton frac on played a crucial role for various fl ow pa erns observed in these beech stands.Abbrevia ons: LLA, log-linear analysis; MCF, matrix-controlled fl ow; SCF, surface-controlled fl ow.
While matrix fl ow enhances various interactions between water and solutes withfi ne earth, preferential fl ow substantially reduces the contact time and area between the liquid and solid phases. Th us, both fl ow types have the potential to either promote or compromise various ecosystem services provided by forests, such as buff ering the alkaline dust imission load in soils (Pichler et al., 2006), waste water purifi cation (Kermen and