Action

Cut large trees/shrubs to maintain or restore disturbance

How is the evidence assessed?
  • Effectiveness
    60%
  • Certainty
    45%
  • Harms
    5%

Source countries

Key messages

  • Two studies evaluated the effects, on peatland vegetation, of cutting large trees/shrubs to maintain or restore disturbance. One study was in a forested fen and one was in an open fenN.B. Cutting large trees/shrubs in peatlands with no history of disturbance is considered as a separate action.
  • Plant community composition (1 study): One before-and-after, site comparison study in a fen in Poland found that in an area where shrubs were removed (along with other interventions), the plant community composition became more like a target fen meadow.
  • Characteristic plants (1 study): One before-and-after, site comparison study in a fen in Poland found that in an area where shrubs were removed (along with other interventions), the abundance of fen meadow plant species increased.
  • Vegetation cover (1 study): One replicated, paired, controlled study in forested fen in the USA found that cutting and removing trees increased herb cover, but had no effect on shrub cover.
  • Vegetation structure (1 study): One replicated, paired, controlled study in a peat swamp in the USA found that cutting and removing trees increased herb biomass and height.

About key messages

Key messages provide a descriptive index to studies we have found that test this intervention.

Studies are not directly comparable or of equal value. When making decisions based on this evidence, you should consider factors such as study size, study design, reported metrics and relevance of the study to your situation, rather than simply counting the number of studies that support a particular interpretation.

Supporting evidence from individual studies

  1. A replicated, paired, controlled study in 2002–2007 in a forested fen in New York State, USA (Scanga & Leopold 2012) found that in areas where trees were felled and removed, herb cover, height and biomass were greater than in adjacent forested areas, whilst shrub cover was similar. After 4–5 years, cleared areas had greater cover than adjacent forested areas of forbs (66 vs 44%) and sedges (9 vs 3%). There was a similar, but non-significant, trend for cover of grass-like plants overall (cleared: 50%; forested: 34%) and ferns (cleared: 17%; forested: 9%). Shrub cover did not significantly differ between areas (cleared: 9%; forested: 10%). In cleared areas, herbs were taller overall (cleared: 44; forested: 25 cm) and produced more biomass (cleared: 68; forested: 21 g/0.25 m2). In spring 2002 and 2003, all trees were cut and removed from 11 circular areas (5 m radius) in a forested fen. This mimicked historical human disturbance. For each cleared area, a forested area <40 m away provided a control. In August 2007, vegetation was surveyed in each area within nine 0.25 m2 quadrats.

    Study and other actions tested
  2. A before-and-after, site comparison study in 2004–2009 in a degraded fen in Poland (Kotowski et al. 2013) found that in an area cleared of shrubs (then rewetted and mown), the plant community composition changed in favour of fen meadow and wet meadow species. Over five years, the overall plant community composition in the managed area became more similar to a target fen meadow vegetation (data reported as a graphical analysis; change not tested for statistical significance). The abundance of fen meadow and wet meadow species, including sedges Carex spp., increased in the managed area but did not change in the target area (data reported as an abundance index). In 2004, willow Salix cinerea shrubs were cleared from 0.7 ha of drained, overgrown fen. The area was then mown annually and rewetted. The study does not distinguish between the effects of these interventions. The managed area was compared to 0.9 ha of target, shrub-free, fen meadow vegetation (retained in depressions during the drained period, but also affected by the rewetting and mown every other year). Annually between 2004 (before shrub clearance) and 2009, cover of every plant species was estimated in 18–22 plots/area. Plots were 20 x 20 m.

    Study and other actions tested
Please cite as:

Taylor N.G., Grillas P. & Sutherland W.J. (2018) Peatland Conservation. Pages 329-392 in: W.J. Sutherland, L.V. Dicks, N. Ockendon, S.O. Petrovan & R.K. Smith (eds) What Works in Conservation 2018. Open Book Publishers, Cambridge, UK.

Where has this evidence come from?

List of journals searched by synopsis

All the journals searched for all synopses

Peatland Conservation

This Action forms part of the Action Synopsis:

Peatland Conservation
Peatland Conservation

Peatland Conservation - Published 2018

Peatland Conservation

What Works in Conservation

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