Manage heathland by cutting

Overall effectiveness category Evidence not assessed
Number of studies: 3
Share Tweet Email

View assessment score

How is the evidence assessed?

Effectiveness

not assessed
Certainty

not assessed
Harms

not assessed

Calculating overall effectiveness category

Background information and definitions

Heathland, like other open habitats, requires some disturbance to maintain habitat favourable to specialist species of butterflies and moths. Management by cutting is one option for creating this disturbance, but cutting causes a sudden change in the habitat structure, potentially removing nectar resources or injuring or killing eggs, caterpillars or pupae living within the heath (Humbert et al. 2010, Morris 2000). Therefore, the timing and frequency of cutting may be important for avoiding these short-term negative impacts on butterflies and moths (Morris 2000). This action includes studies comparing different cutting regimes, as well as studies comparing cutting to other options for heathland management, such as burning.

For studies on the creation or restoration of heathland or shrubland by either multiple actions (which may include cutting) or where the specific action is not clear, see “Restore or create heathland/shrubland”. For studies on other actions for heathland and shrubland management and restoration, see “Replant native vegetation”, “Employ areas of semi-natural habitat for rough grazing (includes salt marsh, lowland heath, bog, fen)” and “Natural system modifications – Use prescribed fire to maintain or restore disturbance in grasslands or other open habitats”.

_{Humbert J.Y., Ghazoul J., Sauter G.J. & Walter T. (2010) Impact of different meadow mowing techniques on field invertebrates. Journal of Applied Entomology, 134, 592–599.}

_{Morris M.G. (2000) The effects of structure and its dynamics on the ecology and conservation of arthropods in British grasslands. Biological Conservation, 95, 129–142.}

Study locations

Key messages

Three studies evaluated the effects on butterflies and moths of managing heathland by cutting. Two studies were in the USA^1,2 and one was in the UK³.

COMMUNITY RESPONSE (0 STUDIES)

POPULATION RESPONSE (3 STUDIES)

Abundance (3 studies): One site comparison study in the USA² found that a pine barren managed for 13 years by mechanical cutting had a higher abundance of Karner blue butterflies than barrens managed by rotational burning or unburned refuges. One before-and-after study in the USA¹ found that the abundance of five butterfly species did not change after the management of a pine barren was changed from rotational burning to unintensive cutting. One before-and-after study in the UK³ reported that the abundance of high brown fritillary and small pearl-bordered fritillary increased after scrub cutting, along with tree felling, coppicing and grazing.

BEHAVIOUR (0 STUDIES)

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

A before-and-after study in 1988–1996 on a pine barren in Wisconsin, USA (Swengel & Swengel 1997) found that the abundance of five butterfly species did not change following the initiation of unintensive cutting instead of burning management. In the first three years after cutting commenced, the abundance of frosted elfin Callophrys irus (1.3 individuals/hour), Olympia marble Euchloe olympia (18 individuals/hour), Karner blue Lycaeides melissa samuelis (120 individuals/hour), Persius duskywing Erynnis persius (1.8 individuals/hour), and dusted skipper Atrytonopsis hianna (1 individual/hour) were all similar to under the previous burning regime (frosted elfin: 0; Olympia marble: 6; Karner blue: 135; Persius duskywing: 0.7; dusted skipper: 0 individuals/hour). In April 1988 and 1991, an area of pine barren was burned. In April 1994, the area was not burned, and unintensive cutting management commenced. Between 1988–1996, butterflies were surveyed along a transect at the site multiple times/year (no further details provided).
Study and other actions tested
Referenced paper
Swengel A.B. & Swengel S.R. (1997) Co-occurrence of prairie and barrens butterflies: Applications to ecosystem conservation. Journal of Insect Conservation, 1, 131-144.
A site comparison study in 1992–2005 in a pine barren in Wisconsin, USA (Swengel & Swengel 2007) found that an area managed by mechanical cutting supported more Karner blue butterflies Lycaeides melissa samuelis than areas managed by rotational burning. Over 13 years, in an area managed by cutting, Karner blue abundance (28–32 individuals/year) was higher than in areas managed by rotational burning (9–11 individuals/year) or rotational burning and cutting (8–10 individuals/year). An unburned refuge supported a similar abundance of Karner blue (11–14 individuals/year). Within a 12,180-ha pine barren, six areas with a similar abundance of wild lupine Lupinus perennis were compared. One area was managed by mechanical cutting, one was managed with cool-season rotational burning, three were managed by burning and cutting, and one area was left as a 14-ha unburned refuge (last burned in 1988). From May–July 1992–1995 and 1997–2005, butterflies were surveyed once/year along transects in each area.
Study and other actions tested
Referenced paper
Swengel A.B. & Swengel S.R. (2007) Benefit of permanent non-fire refugia for Lepidoptera conservation in fire-managed sites. Journal of Insect Conservation, 11, 263-279.
A before-and-after study in 2002–2011 in an area of heathland, woodland and grassland in South Wales, UK (Hobson and Smith 2012) reported that after scrub cutting was conducted, along with tree felling, coppicing and grazing, the number of high brown fritillary Argynnis adippe and small pearl-bordered fritillary Boloria selene increased. Results were not tested for statistical significance. In 2002, prior to scrub control, an average of seven high brown fritillary adults/hour were recorded at the site, and seven years after scrub clearance began, 14 adults/hour were recorded. Small pearl-bordered fritillary also increased in number between 2003 and 2011 (numbers not given). From 2003–2011 some patches of bracken Pteridium aquilinum, bramble Rubus fruticosus agg., honeysuckle Lonicera periclymenum and tree saplings were cut back in the Alun Valley, a 254 ha landscape comprising heathland, woodland and grassland. Tree felling (2003–2011), coppicing of hazel Corylus avellana and gorse Ulex europaeus (1999–2011) and sheep grazing (start date not given–2011) were also conducted in areas of the site. Adult butterflies were counted annually from 2002–2011.
Study and other actions tested
Referenced paper
Hobson R. & Smith R. (2012) High Brown Fritillary in the Vale of Glamorgan: saving the last site in Wales. Pages 52-57 in: S. Ellis, N.A. Bourn & C.R. Bulman (eds.) Landscape-scale conservation for butterflies and moths: lessons from the UK. Butterfly Conservation.

Please cite as:

Bladon A.J., Bladon, E. K., Smith R.K. & Sutherland W.J. (2023) Butterfly and Moth Conservation: Global Evidence for the Effects of Interventions for butterflies and moths. Conservation Evidence Series Synopsis. University of Cambridge, Cambridge, UK.

Where has this evidence come from?

List of journals searched by synopsis

All the journals searched for all synopses

This Action forms part of the Action Synopsis:

Butterfly and Moth Conservation

Related Actions

Actions	Effectiveness	Studies	Category
Restore or create habitat connectivity Action Link	Evidence not assessed	6	Synopsis Link
Maintain or create bare ground Action Link	Evidence not assessed	4	Synopsis Link
Coppice woodland Action Link	Evidence not assessed	10	Synopsis Link