Introduction

Project description
In 2009, a noctule Nyctalus noctula maternity roost (≤75 bats) was recorded in a tree, accidentally felled in 2011 over public safety concern. Rapid response mitigation returned a noctule maternity colony in 2012 and 2013. This case study exemplifies the need for sharing ecological data within organisations and third parties.
Ecologist’s name and contact details
Name: Chris Damant. Company: Bernwood ECS Ltd. Address: Hensmans Farmhouse, Nearton End, Swanbourne, MK17 0SL. Email: chris@bernwood.net. Mobile: 07817131683.
Site postcode
MK5 6FQ
Planning authority
Milton Keynes Council
Brief site description
The noctule maternity roost was found inside an ash Fraxinus excelsior tree with a central rot hole. Woodpecker holes allowed bat access into the central rot hole. The tree was situated on the edge of a ride on the north side of ancient semi-natural woodland. The ancient semi-natural woodland is approximately 25 ha in area, with approximately 6 ha of buffer around it. It has a canopy mainly composed of ash and oak and an understory of hazel. It is located in south western Milton Keynes, and the woodland cover in this area was recorded in the Domesday Book of 1086.

Pre-works roost structure

Type of structure
Other
Use
Other
Approx. age
<100 years
Main construction material of walls
Other
Roof design
No Roof Applicable (Tunnel or Bridge)
Roof material
Not Applicable
Internal roof structure
Not Applicable
Lighting present on site and its proximity to the roost
No lighting on site.
Photos or annotated figures of roost structure

Pre-works roost description

Species
Noctule
Number of bats max count
75
Type of roost
Maternity Roost
Evidence of bats
Bats Recorded Emerging/Re-entering
Roost location
Other
Aspect of roost
Various
Height of roost entrance (m)
Various; 2-3 m.
Roost material(s)
  • Other
Nearest commuting feature
Woodland
Distance to nearest commuting feature (m)
0 m; woodland ride adjacent.
Photos or annotated figures of roost

Proposed works

Description of works
Contract staff operating on behalf of the landowner were employed to conduct routine ride side and tree safety management work. The contractors determined the ash tree to be a public safety concern due to characteristics of internal rot and inclination over the main woodland ride. Two grey squirrel emergences from the tree led to the contractor’s assessment that the tree was not suitable as a bat roost, and the tree was felled. Upon learning what occurred, the landowner halted the processing of the timber and contacted Bernwood ECS Ltd. for designing and implementing bat mitigation and compensation schemes. Within hours of the felling, the roost was confirmed vacant, Natural England was informed of the events, and a rapid-response mitigation strategy with training programme agreed.
Type of impact upon the roost
Long-Term Roost Modification and Roost Loss

Proposed mitigations

Type of mitigation
Mitigation
Specific technical detail of measure
Survey information from 2009 and 2011 along with photographs and night-shot video footage were used to identify bat access points including their heights and orientations. The mitigation involved reinstating the trunk against the nearest suitable tree, also ash. A high lift was used to assist with the lifting of the felled trunk, fastening it to the live ash tree using 19mm steel banding. Protective rubber straps were placed between the steel banding and both tree trunks to reduce the impact on the live tree. The access points were orientated to recreate their original positions prior to felling. A replacement top was constructed from ash wood to shelter the roost, to replicate internal environmental conditions, and to prevent an increase in decay through weathering. The top was similarly bonded to the trunk with steel straps. The reinstated section plus top totalled 3.4m tall by 0.5m wide (1.1m wide when attached to the live tree). The works took place over five consecutive days after the tree’s felling.

Other compensation measures were implemented, such as five Schwegler woodcrete 2FN bat boxes and cavities carved into nearby ash trees to stimulate rot (the crown weight reduced to maximise tree longevity). No post-development monitoring of these measures was not conducted by Bernwood ECS Ltd.
Relevant annotated figures
Roost location
Other
Aspect of roost
N
Height of roost entrance (m)
Various; 2-3 m.
Roost material(s)
  • Other
Nearest commuting feature
Woodland
Distance to nearest commuting feature (m)
0 m; woodland ride adjacent.
Photos or annotated figures of roost

Monitoring data

Length of monitoring proposed
2 years post-development.
Frequency of monitoring
Annually.
Type of monitoring
Dusk and Dawn Survey
Date and time
8th July 2012 22:00
Evidence recorded
37 noctules recorded emerging in 2012. Video evidence on YouTube: 1) https://youtu.be/J-t6Rmehscg and 2) https://youtu.be/vhGKF24UmpQ
Interventions made
None.
Type of monitoring
Dusk and Dawn Survey
Date and time
27th May 2013 22:00
Evidence recorded
46 noctules recorded emerging in 2013. Video evidence on YouTube: https://youtu.be/0dg_0kVNJQ4
Interventions made
None.

Final details

Lessons learned
This case study highlights the advantage of resourceful, time-sensitive responses to accidental damage of ecologically important sites. The rapid response of the landowner improved the prospect of delivering a creative conservation strategy with positive results. The landowner also reduced the likelihood of future incidents through addressing weaknesses in operational structure, specifically through communication channels within the organisation itself and with third parties conducting works. This case study also underscores the value of biological recording and photographic evidence, as it significantly improved the effective delivery of mitigation by ensuring correct bat access point heights and orientations.
This work has since been published in Conservation Evidence to inform practitioners on tree roost displacement:
Damant C. & Dickins E. Rapid response mitigation to noctule Nyctalus noctula roost damage, Buckinghamshire, UK. Conservation Evidence (2013) 10, 93-94.

The landowner has continued informal monitoring of all implemented measures since 2013. A 2020 update is included:
• The tree roost mitigation structure was used by roosting noctules (and possibly breeding) quite a bit and Paul Moon and myself monitored it informally. We last had bats in there, for certain, in June 2017.
• Noctules have never been found any of the bat boxes provided.
• we now know of six trees, all ash, which are used as roosts from time to time. but there are three ash trees in the northern section with woodpecker holes, which now seems to be the main concentration.
• One of the trees used by noctules is situated about 10 metres behind the original roost tree but it is not possible to confirm this was one of the trees that were cut to create artificial cavities in the area of the roost.
'the mitigation was shown to work in the short term and allowed the noctule colony time to adapt to more favourable alternative roosts in trees with woodpecker holes within the woodland.'

M. Kincaid. The Parks Trust. Pers. comm. 2020