What Counts as a Forest Under EUDR?

The definition combines thresholds and land use

Under Article 2(4), forest means land spanning more than 0.5 hectares with trees higher than five metres and canopy cover above ten per cent, or trees able to reach those thresholds in situ, excluding land predominantly under agricultural or urban use. These elements must be considered together.

A tree-cover map is therefore useful evidence, but not the definition itself. Tall trees in an agricultural plantation can be excluded, while a temporarily unstocked forest area can still require forest treatment where the characteristics and expected regeneration support it. Actual land use and historical context matter.

This classification underpins the EUDR deforestation-free requirement. Use the binding Article 2(4) wording alongside the interpretive July 2026 Commission guidance, particularly for borderline areas.

Apply area, height and canopy together

The statutory thresholds describe a land area and tree stand, not a single isolated tree. Assess the relevant extent, the trees' height and canopy cover, or their capacity to reach the thresholds in place. Do not combine an area measurement from one boundary with canopy data from an unrelated larger landscape.

The guidance explains the simultaneous assessment of these characteristics, including young trees expected to develop. Record the measurement source, observation date, resolution and any uncertainty. Near a threshold, a coarse map or rounded estimate may require additional information before a confident conclusion is possible.

The Regulation says more than 0.5 hectares and more than ten per cent canopy cover. Avoid rounding a borderline observation into a definitive statutory outcome. Where the guidance's explanatory phrasing and measured facts leave a material question, preserve the exact binding wording and obtain a fact-specific clarification.

Predominant agriculture and urban use are excluded

Article 2(4) excludes land predominantly under agricultural or urban use. Agricultural plantations and agroforestry systems therefore need analysis of actual purpose and management, even when the trees satisfy physical thresholds. Urban parks and gardens are discussed in the guidance as examples where urban use can predominate.

This does not let a whole agricultural property erase a qualifying forest section. The guidance says to assess forest and agricultural areas within the same plot separately. The relative proportion of the wider property is not a reason to ignore the forest part.

Distinguish predominant land use from occasional activity. Limited side production or occasional extensive grazing within forest does not necessarily make agriculture predominant. Conversely, established agricultural systems with shade trees should not automatically be classified as forest solely because a tree-cover layer shows a dense canopy.

A current opening can still be forest

Temporary lack of tree cover can reflect harvesting, natural disturbance or young regeneration rather than a change in land use. The guidance expressly discusses temporarily unstocked areas expected to regenerate. Forest management records, inventories and the observed regeneration sequence can help explain the classification.

A current image showing bare ground is therefore not enough to label the land non-forest. Establish the previous state, reason for the opening, management context and subsequent or expected development. If agriculture replaces the forest, the conversion question must then be assessed separately.

Abandoned agricultural land and temporary fallow require particular care. The guidance describes circumstances and evidence concerning continuing agricultural use and regeneration. Do not apply a simple rule that every unused field becomes forest after a fixed number of years without checking the complete facts and relevant guidance.

Administrative labels are evidence, not the whole test

The guidance says actual forest properties should prevail over designation in land registers and cadastral maps. A plot outside legally designated forest land can still meet the EUDR forest definition. An agricultural registration may record a current administrative category rather than the historical physical condition.

Such records remain useful. They can help show earlier agricultural use, management obligations or why a temporarily unstocked area remains forest. Compare them with dated imagery and other evidence, recording what each source actually establishes rather than treating one document as conclusive for every issue.

The EU Observatory's forest information can also support assessment, but the guidance describes it as non-exclusive, non-mandatory and without legal value. Operators may use appropriate alternative information. A public map result should therefore be interpreted and documented, not presented as official approval of a source plot.

Consider a supplier polygon containing established farmland and an adjacent wooded section. Measure and assess the wooded section on its actual characteristics, rather than averaging canopy across the whole holding. Then examine whether that section was forest at the relevant historical point and what happened afterward. An agricultural label for the wider holding is useful context but cannot replace this separate assessment of a potentially qualifying area.

Record the classification before assessing conversion

A forest assessment should identify the area, date, physical characteristics, predominant land use, sources and reasoning. Where the question concerns conversion after 2020, reconstruct the relevant earlier classification rather than recording only what is visible today. Keep uncertainties and supplementary checks in the file.

The article on tree cover versus forest explains common map-reading mistakes. Review the classification if boundaries, observation quality or credible historical evidence changes, especially where a result sits near the legal thresholds.

A correct forest classification answers the starting-point question. It does not alone establish that a commodity is compliant: later agricultural conversion, wood-specific degradation, lawful production and the other EUDR requirements must be assessed separately.