Data from: Dataset on stand structure in hemiboreal forests across management histories and stand ages

Please cite this dataset as: Rosenvald, R., Lõhmus, A., Kont, R., Kraut, A., Lõhmus, P., Remm, L., Tekko, T., Vaikre, M., Runnel, K.2026. Dataset on stand structure in hemiboreal forests across management histories and stand ages. Data in Brief, 112688. https://doi.org/10.1016/j.dib.2026.112688

Data description. This dataset compiles detailed representative forest stand structure data from a European hemiboreal forest region; it spans multiple forest types, successional stages, and forest management contexts. It integrates measurements of live trees and dead wood, including fallen trunks, snags (standing dead trees), stumps and fine woody debris (down to 3 mm diameter), together with tree species identity, dimensional attributes, and decay stages. A subset of stands has been surveyed repeatedly, capturing temporal changes in forest structure.

Study area. Estonia, hemiboreal forest zone. Field sampling was conducted between 2006 and 2024.

Data coverage. The dataset comprises detailed stand-structure measurements from approximately 600 forest stands, the most used designs representing 2-ha plots. It includes most common hemiboreal forest types along gradients of dominant tree species and soil moisture. These range from low-productivity, dry Scots pine–dominated forests to black alder–dominated mobile-water swamps, with particularly strong representation of productive Norway spruce–deciduous mixed forests and drained peatland forests. Stand ages range from a few years post clearcutting to old stands with the dominant tree layer >200 years old. Old stands without signs of management are well represented (98 study stands) and constitute a substantial reference set for naturally developing and old-growth forests in the region. The stands encompass a broad range of silvicultural treatments, including post-clearcut and post retention-cut successions, mature forests with sanitary cuttings, stands subject to precommercial and commercial thinning, and shelterwood cutting. In addition, a subset of stands includes repeated measurements of forest structure following ditch closure (rewetting) as part of a peatland forest restoration experiment.

Methods. Live trees, standing dead trunks and stumps were recorded along strip pl