Part two: management, non-intervention and responsibility in private woodland

*This is Part Two of a two-part series about woodland ownership and responsibility. It follows directly from Part One, Who is responsible for the UK’s woodlands?, which considers the case for a national woodland register: a durable means of identifying the responsible person for each woodland and carrying knowledge across changes of ownership. If you have not read Part One, it is best to begin there before continuing. Part Two continues from this point. If a woodland register tells us who is responsible, should that responsibility include an obligation to plan for the woodland’s future?*

A register of owners and a requirement to manage woodland are distinct aspects. There is also a critically important related issue: an explicit expectation that an owner should assess the woodland, state their objectives and make a considered decision about its future, without being required to carry out a predetermined set of operations.

That distinction matters because bringing woodland ‘into management’ is often taken to mean visible activity: thinning, coppicing, harvesting, planting, controlling vegetation or improving access. Yet deliberate non-intervention may be the appropriate course for an ancient woodland feature, a minimum-intervention reserve, veteran trees, deadwood-dependent species or a stand being allowed to develop greater structural complexity. The distinction is therefore not between action and inaction, but the deliberate and considered decision by a land owner to do the best thing for their woodland.

Planning is not the same as intervention

A credible woodland plan (i.e. a plan compliant with UK Forestry Standard) should be able to say: these are the owner’s objectives; this is what is known about the woodland’s condition, these are the environmental and economic risks; this is why intervention or non-intervention is intended; these are the circumstances that would prompt reconsideration; and this is when the decision will be reviewed.

The UK Forestry Standard: The UKFS defines the government requirements for forestry in the UK. It provides a basis for regulation and monitoring, including national and international reporting.

Based on this definition, planned non-intervention should absolutely be considered ‘management’. It is not the same as a woodland receiving no assessment because its owner lacks knowledge, confidence, time or contact with advice. There is ecological evidence for preserving this distinction. A European meta-analysis found slightly greater overall species richness in unmanaged forests, with particularly positive responses among organisms dependent on continuity, deadwood and large trees, although responses differed substantially between taxonomic groups (Paillet et al., 2010). Conversely, non-intervention may be unsuitable where deer browsing prevents regeneration, invasive species are spreading, unstable trees threaten people, fuel loads create acute wildfire risk, or pests and diseases require containment. Neither intervention nor restraint is inherently responsible without reference to place, evidence and objectives, and all these are the responsibilities of the woodland owner.

Research on supposedly ‘passive’ owners reinforces the point. Interviews with 273 Finnish owners classified as ‘passive’ found that only about one-third were fully passive in both management and timber sales. Many of the remainder used their forests for household, recreational, heritage or environmental purposes that official activity measures failed to capture (Matilainen and Lähdesmäki, 2023). Research in southwestern France similarly found diverse practices and degrees of engagement hidden within the category of ‘inactive’ owner (Brahic, Banos and Deuffic, 2025). Recent Canadian research makes the distinction clearer still. In a national survey of 611 private owners and practitioners, ‘laissez-faire’ was the most favoured of six possible climate-adaptation strategies. Yet 95 per cent of respondents intending to use this approach were already actively managing their forests, while 74 per cent of all respondents intended to combine two or more adaptation strategies. Restraint could therefore sit within an active programme of observation and adaptation rather than represent its absence (Fouqueray et al., 2026). The study measured intentions rather than subsequent behaviour and its sample was not fully representative, but it is a useful warning against inferring management quality from the visibility of operations.

Such evidence makes a stronger case for management planning. A proportionate planning requirement could ask an owner to make their reasoning explicit without presuming that timber production or physical intervention is the desired outcome. The relevant evidence is not simply whether something was done, but whether objectives were explicit, risks were considered, the decision was informed and circumstances were later reviewed.

The case for a woodland management plan.

What might a planning responsibility involve?

The obligation to have a management plan could be scaled to the woodland. A short management statement may be sufficient for a small, low-risk woodland, while a large, complex or high-risk holding may justify a fuller plan. At its simplest, the statement might contain:

the owner’s objectives;
a basic description of condition and significant risks;
the intended approach, including any areas of deliberate non-intervention;
the evidence or advice informing that choice;
circumstances that would trigger reconsideration;
a review date.

This would exist as a record of duties to assess and explain desired outcomes, not necessarily as an instruction to physically intervene. A separate duty might be justified where inaction creates material risks beyond the property boundary, including defined biosecurity, wildfire or public-safety risks. The evidential threshold and safeguards would need to be correspondingly stronger.

The distinction suggests a possible sequence: registration establishes contact; the woodland record preserves knowledge; planning makes objectives and reasoning explicit; and intervention is required only where justified by specified outcomes or material risks. Collapsing these stages into a single concept of ‘active management’ would obscure important choices about evidence, proportionality and property rights.

Lessons from other countries

There is perhaps no perfect international model waiting to be applied to the UK. Several systems nevertheless illuminate what helps a management plan influence decisions in a woodland, who planning programmes tend to reach, and where compulsion encounters practical limits.

France: proportional planning, but persistent gaps

France offers the clearest example of a statutory threshold. Private forests of 20 hectares or more are generally required to have an approved Plan Simple de Gestion, normally covering ten to twenty years. The threshold was recently reduced from 25 hectares by France’s 2023 wildfire legislation. The plan describes the forest, the owner’s objectives and the proposed programme of felling and other forestry works. Smaller holdings can use lighter voluntary documents.

The model establishes proportionality and continuity, but it has not solved the wider engagement problem. A 2024 inter-ministerial review reported that only 27 per cent of French private-forest area was covered by a sustainable-management document and that the proportion had been broadly stable for four decades. France has 3.5 million private forest owners, many with holdings outside the mandatory threshold. Significantly, the review advised against extending compulsory plans below 20 hectares. Documents alone would not overcome the poor economics of small-scale working and might generate costs that owners could not recover. It favoured territorial facilitation, voluntary forest-management associations and concerted plans across holdings. France demonstrates both the value and the limit of a mandate: it can establish discipline above a threshold, but cannot itself make fragmented woodland operationally or economically manageable.

Ontario: planning as a reciprocal bargain

Ontario offers a different route. Its Managed Forest Tax Incentive Program is voluntary, but participating owners receive a substantial reduction in property taxation on eligible forest land. In return, they must prepare a ten-year managed-forest plan, have it approved by a qualified independent professional following a site visit, follow good forestry practices and submit a progress report after five years.

The programme connects planning to a continuing bargain rather than treating it as an isolated administrative demand. Eligible stewardship is not confined to harvesting or silviculture. It can include wildlife work, monitoring, learning about the forest and protecting environmentally sensitive areas by limiting disturbance. Deliberate restraint can appear as a positive management choice, while continued inactivity that degrades forest health is treated as a risk requiring action.

The number of enrolled properties approximately doubled between 2004 and 2024, from 10,500 to 21,200, while the area covered rose more modestly, from 724,900 to 879,000 hectares. Of course, these figures demonstrate take-up of the scheme, not ecological additionality. Participating owners may already be more inclined towards stewardship, and programme statistics do not establish what would have happened without the incentive. Even so, Ontario poses a useful question for the UK: should planning be imposed as an unconditional requirement of ownership, or requested as one side of an explicit exchange involving taxation, grants, professional help or regulatory simplification?

Norway: having a management plan is not the same as enacting it

Norwegian forest management plans are voluntary, typically renewed every 15 to 20 years, and are subsidised and commonly organised across municipalities. They combine maps and timber inventories with management proposals and the identification of important environmental habitats.

A representative survey found that 37 per cent of non-industrial private owners had a plan. Of those owners, 66 per cent knew its contents well, but only 40 per cent reported implementing its proposals. The strongest predictor of use was not possession of the management plan itself but whether owners considered it relevant to their objectives. Perceived fit increased the probability of implementation by 38 percentage points, while contact with municipal forestry advice increased it by a further 13 points (Bashir, Sjølie and Solberg, 2024).

A compulsory plan could therefore produce administrative coverage without changing decisions. Planning is most likely to matter when it is prepared closely with the owner’s participation, reflects multiple objectives, contains usable information and is connected to continuing advice. The document should embody a decision process, not become the final outcome.

United States: who receives help, and what happens afterwards?

The United States Forest Stewardship Program supports state agencies to provide family forest owners with voluntary, multi-resource plans, education and technical assistance. It resembles the supportive infrastructure that might sit around a UK planning system more closely than it resembles a regulatory requirement.

Its evaluation has revealed two key problems that participation figures might mask. One major limitation is that reach is limited and selective. A national study found that the programme reached only a small fraction of eligible owners. Recipients differed from other owners in their characteristics, objectives and existing actions, while traditional assistance was generally not converting inactive owners into active managers. Earlier participant surveys reported high satisfaction and that more than 80 per cent had begun implementing their plans, but participants were also disproportionately white and relatively well educated (Butler et al., 2014). A programme can appear successful among its users while continuing to miss precisely the owners that policy instruments most want to reach. Another issue experienced under this program is that a plan may be less influential than help of guidance at the point of intended action. Monitoring of 174 timber harvests on family-owned land in Minnesota found that possession of a management plan was associated with only modest differences in environmental best practice. Professional supervision of the timber sale had the strongest association with better practice, particularly around water and riparian protection (Wilson, Kilgore and Snyder, 2022). The policy instrument should therefore focus strongly on the continuing relationship between owner, woodland record and trusted adviser, rather than the plan as a completed document which may sit on a shelf gathering dust.

Spain and Finland: collective capacity and trusted institutions

Spain is the clearest example of the fourth aspect described in Part One: a duty to act, not merely to register or complete a management plan. Spanish forest law, administered through the autonomous regions, obliges both public and private owners to carry out preventive treatments set out in regional forest plans. Where an owner fails to act, the regional administration can carry out the work itself and recover the cost from the owner. It is a genuine action obligation, backed by a state fallback power, extending well beyond an information or planning requirement.

Spain also demonstrates why some woodland risks cannot be managed parcel by parcel. Evidence from Galicia and Catalonia suggests that resilience to wildfire depends on local organisation and social learning as well as formal powers. More resilient communities combined local knowledge, collective organisation and deliberate fuel or fire management (Marey-Pérez et al., 2021; Rodríguez-Carreras et al., 2020). A register might locate neighbouring owners and plans might identify risks, but neither would supply the institutions needed to coordinate action. Even Spain’s statutory fallback power depends on regional administrations having the capacity to deploy it. That combination, a duty to act paired with a reality check about whether the state can actually enforce it, is an important illustration in this thinkpiece series of why an action obligation is a much larger undertaking than a register or a planning duty.

Finland offers a related lesson about trusted delivery. For decades, private owners financed regional Forest Management Associations through a compulsory, tax-like fee. The associations advised owners, arranged silvicultural work and timber sales, and represented their interests. The fee ceased in 2014 and compulsory membership ended in 2015, after which the associations relied on voluntary membership and service income. A forestry-sector account reported that about 80 per cent of private owners remained members afterward (Finnish Forest Association, 2016). This is not an independent evaluation, but it suggests that much of the institutional value survived after compulsion ended.

Together, Spain and Finland show that information and plans require social infrastructure. Owners need organisations capable of translating intentions into practical work, coordinating across boundaries and sustaining trust over time.

What the international case studies suggest

Seven design principles emerge:

Separate planning from prescribed action. A plan should be able to justify intervention, restraint or a combination of both.
Scale requirements to size, complexity and external risk. The same document should not be expected from a small amenity woodland and a large commercial holding.
Record *deliberate* non-intervention as a positive decision. It should include objectives, evidence, review points and triggers for reconsideration.
Reflect owner objectives as well as public interests. Plans that owners regard as irrelevant are unlikely to guide positive behaviour.
Connect responsibility to a credible reciprocal offer. Advice, financial support, tax treatment or regulatory simplification may be needed to make planning legitimate and useful.
Invest in trusted professional and collective capacity. The management plan is the beginning of a relationship, not justification for added bureaucratic burden.
Evaluate reach and outcomes, not document production. High satisfaction among participants may conceal selection bias, while management plan coverage says little about woodland condition.

A proportionate route to testing the concept

As argued in the first article, a woodland register could provide a gateway through which owners are identified, records retained and support offered. It need not immediately trigger a universal duty to produce a full management plan.

A staged test or pilot could begin when a woodland changes ownership, enters a public scheme, passes a certain size or reaches a defined risk threshold. The first requirement might be a proportionate management statement covering objectives, basic condition and risk, the reasoning for intervention or non-intervention, and a review date. Larger, more complex or higher-risk holdings could require a fuller management plan. Stronger duties to act should be tied to demonstrable external risk or defined outcomes rather than woodland ownership alone.

The test should ask:

Does it reach owners absent from existing forestry systems?
Are reported benefits additional, or do they reflect the self-selection of owners who were already knowledgeable and active?
Does planning clarify intentional non-intervention as well as necessary action?
Do owners understand, use and revise their woodland management plans?
Does professional support continue when decisions are implemented?
Do plans lead to measurable improvements in resilience, condition or risk management?
Does the system enable cooperation across property boundaries?
Are burdens proportionate, especially for small and low-risk holdings?
Does it reduce what government currently expends identifying and re-identifying owners, or simply add a further layer of process on top of existing costs?

The crucial point is that registration is not management planning, having a management plan does not necessarily lead to intervention, and intervention is not necessarily good management.

In the first article in this thinkpiece series, Who is responsible for the UK’s woodlands?, I argued that the UK should at least debate a durable way of identifying woodland owners and preserving knowledge across changes of ownership. This second article reaches a related but distinct conclusion. If responsibility is to mean more than appearing on a database or register, a proportionate expectation to assess and plan may be defensible. But the objective should be considered and deliberate woodland stewardship, not visible activity or paperwork for its own sake.

The central question is therefore not whether every woodland owner should be required to manage in a prescribed way. It is whether every woodland would benefit from an informed decision about its future, and whether owners can be given the knowledge, support and freedom needed to make that decision well.

The prospect of catastrophic ecosystem collapse in the next 50 years (Tew et al. 2024) may be seen by many as sufficiently compelling to consider the prospect of woodland registration and deliberate environmental stewardship as an urgent priority in the UK.

Should woodland ownership carry an obligation to plan?

Part two: management, non-intervention and responsibility in private woodland

Planning is not the same as intervention

What might a planning responsibility involve?

Lessons from other countries

France: proportional planning, but persistent gaps

Ontario: planning as a reciprocal bargain

Norway: having a management plan is not the same as enacting it

United States: who receives help, and what happens afterwards?

Spain and Finland: collective capacity and trusted institutions

What the international case studies suggest

A proportionate route to testing the concept

Further reading

Peer-reviewed research

Policy and statistical sources

Like this:

Should woodland ownership carry an obligation to plan?

Part two: management, non-intervention and responsibility in private woodland

Planning is not the same as intervention

What might a planning responsibility involve?

Lessons from other countries

France: proportional planning, but persistent gaps

Ontario: planning as a reciprocal bargain

Norway: having a management plan is not the same as enacting it

United States: who receives help, and what happens afterwards?

Spain and Finland: collective capacity and trusted institutions

What the international case studies suggest

A proportionate route to testing the concept

Further reading

Peer-reviewed research

Policy and statistical sources

Share this:

Like this: