Nutrient dynamics along a rotation of Douglas-fir was studied by chemical characterisation of solutions that are transferred through the ecosystem. The chronosequence approach was used to represent the development stages of the forest rotation. Rainfall composition classified the present site as a pristine area. The transfer of precipitations through canopies was characterised by an enrichment of the ionic charge in the solutions, which was related to the washoff of elements deposited on branches and needles (dry deposits) or to the ion-exchange processes between the elements in the internal plant parts and those in the rainfall (canopy leaching). The main source of NO 3 − N, NH 4 + N, SO 4 2− S, Cl −, Na +, Ca 2+, Mg 2+, Al 3+ and H + was considered to be the washoff from plant surfaces. Total organic carbon (TOC), K + and Mn 2+ were considered to originate mainly from leaching. The foliar uptake of nitrogen in the young stand and the parallel leaching of K + from the canopy characterised differences in solution composition between the stands. The concentration increase was more significant in stemflow solutions than in throughfall as a consequence of the input of elements from the bole surface washoff. Differences between stands were related to stem size and to exposure of stems to the deposition of particles and gases. SO 4 2− S, NO 3 − N and Cl − controlled the transfer of nutrients in rainfall, throughfall and stemflow to the same extent. A higher participation of SO 4 2− S in the ionic charge was mainly observed during winter. Soil solution chemistry was the result of a complex combination of factors like soil organic matter content, mineralisation and nitrification capacity and plant nutrient requirement, and was greatly influenced by stand structure and seasonal patterns. The soil organic pool and its potential for mineralisation were the main factors that determined the solution chemistry in all layers, but to different extents. Nitrification was the major process acting on the release of cations from the ion-exchange sites and NO 3 − N was generally the main anion in the soil solutions. SO 4 2− S, occasionally controlled charge neutrality when the NO 3 − N concentration was too low. K + that leached from canopy and from the organic litter influenced the quality of the soil solutions in the young stand down to a depth of 15 cm. Soil organic matter content, and probably the type of organic matter and/or microbiota in each stand were the main factors responsible for differences in the soil solution composition between stands. Although the differences in the soil solution composition were more related to soil characteristics than to stand age, the great differences in the quality of throughfall, stemflow and forest floor solutions were directly related to tree growth and stand characteristics.