What Is Forest Degradation Under EUDR?

EUDR uses a defined set of forest transitions

Forest degradation under EUDR means specific structural changes to forest cover. Article 2(7) covers conversion of primary or naturally regenerating forests into plantation forests or other wooded land, and conversion of primary forests into planted forests. It is not a general label for every decline in forest condition.

The definition matters through Article 2(13)(b): relevant wood must have been harvested without inducing that degradation after 31 December 2020. This is additional to the condition concerning forest conversion to agricultural use. A wood source can avoid agricultural conversion yet still require scrutiny under the degradation rule.

Read this within the complete deforestation-free requirement. The current Articles 2(7) to 2(13) define the categories and the wood condition that uses them.

Identify the starting forest type

Primary forest is naturally regenerated forest of native species without clearly visible indications of human activity and with ecological processes not significantly disturbed. Naturally regenerating forest is predominantly composed of trees established through natural regeneration, with several specific inclusions in Article 2(9).

Those categories cannot always be reliably identified from canopy extent alone. Inventory information, species composition, management history and other suitable evidence may be needed to understand the starting condition. Record the spatial area and historical date to which the classification applies.

Do not assume that the absence of a national primary-forest label establishes absence of the EUDR category. National classifications can support the assessment but may use different definitions. Explain the relationship between the source information and the Regulation's actual terms.

Identify the resulting forest or land category

Planted forest is predominantly established through planting or deliberate seeding, with the specified expectation about growing stock at maturity. Plantation forest is a more specific planted-forest category with intensive management and the characteristics defined in Article 2(11). Not every planted forest is therefore a plantation forest.

Other wooded land is also separately defined. Assessing a transition into that category requires its characteristics, not merely a low-canopy map signal. A temporary observation after harvest may not establish the lasting structural change claimed.

These distinctions affect the listed transitions. Conversion from primary forest into planted forest is covered even where the resulting planted forest is not a plantation. Conversion from naturally regenerating forest into planted forest should not automatically be described as prohibited degradation without checking whether the resulting category and exact Article 2(7) transition are met.

Connect the transition to harvesting and time

The wood condition concerns harvesting without inducing the defined degradation after the cut-off. Establish the harvesting event, affected source area, starting category and resulting transition. A broad regional deterioration statistic can inform risk, but does not itself demonstrate that the particular harvested wood induced a listed change.

Likewise, a harvest permit may establish aspects of legality without resolving the forest-type transition. The product must satisfy the separate deforestation-free and lawful-production conditions. A national authority permitting an operation does not rewrite the EUDR definition.

Keep dates clear. The historical cut-off is not the same as the market application date. Evidence about forest structure and management should cover the period relevant to the harvesting and transition, rather than only the condition when the supplier was first approved.

Choose evidence that can answer the structural question

Satellite imagery can show harvesting patterns, canopy changes and regeneration sequences. However, it may not by itself establish primary-forest characteristics, natural regeneration proportions or the expected composition at maturity. Combine suitable observations with forest inventories, management records and other credible source information.

A certification document can support the assessment only to the extent its scope and underlying criteria address the relevant facts. Check the area, period, audit evidence and connection to the goods. Do not replace the legal transition test with a generic certified or sustainable label.

For mixed-source wood products, identify all relevant source areas and preserve the product links. A reassuring assessment for one forest cannot resolve uncertainty about other wood blended into the same product. Supply-chain records are necessary to know which forest assessments matter.

A practical review can begin with a source described as naturally regenerating forest that is harvested and replanted in regular rows. The rows alone do not establish every plantation-forest criterion, but they justify checking the planting, species, age structure and management evidence. Establish the resulting category and harvesting connection before deciding whether the listed transition occurred. Preserve the earlier inventory and later management information together, since looking only at the current stand can conceal the starting category that makes the transition legally significant.

State the conclusion precisely

Record whether the evidence establishes or excludes a listed transition induced by harvesting, the facts supporting that conclusion and any unresolved uncertainty. Avoid stating that all environmental impacts were absent merely because the narrow EUDR degradation definition was not met.

The wood-product degradation assessment translates the definition into sourcing controls. The Commission guidance can support interpretation, while the Regulation remains the binding source for the categories and condition.

A precise conclusion helps the operator decide whether further evidence or mitigation is needed before it can reach no or negligible risk. It also makes later review possible if new inventory information or corrected harvesting boundaries changes the historical picture.