Action: Translocate bats
Key messagesRead our guidance on Key messages before continuing
- Two studies evaluated the effects of translocating bats on bat populations. One study was in New Zealand and one study was in Switzerland.
COMMUNITY RESPONSE (0 STUDIES)
POPULATION RESPONSE (2 STUDIES)
- Reproductive success (1 study): One study in Switzerland found that a female greater horseshoe bat that settled at a release site after translocation had a failed pregnancy.
- Survival (1 study): One study in Switzerland found that four of 18 bats died after translocation.
- Condition (1 study): One study in New Zealand found that lesser short-tailed bats captured at release sites eight months after translocation were balding and had damaged, infected ears.
USAGE (2 STUDIES)
Translocation involves the transport and release of animals from one area to another. This may be done to protect against threats from introduced predators, competitors or disease, or to supplement existing populations. Previous studies on the homing behaviour of bats have shown that bats will often attempt to fly long distances to return home when released in new areas (e.g. Holland et al 2006).
Holland R.A., Thorup K., Vonhof M.J., Cochran W.W. & Wikelski M. (2006) Bat orientation using Earth's magnetic field. Nature, 444, 702.
Supporting evidence from individual studies
A study in 2005 on Kapiti Island, New Zealand (Ruffell & Parsons 2009) found that nine of 20 translocated lesser short-tailed bats Mystacina tuberculata were recorded at the release site 232 days after release, and all were in poor condition. After eight months, captured bats were balding and had damaged infected ears and were subsequently returned to captivity. Four male and 16 female captive bred juveniles were released on the Island in April 2005 and provided with roosts and supplementary food (consistently for 55 days after release and irregularly for 156 days after release). Kapiti Island is a 1,965 ha nature reserve of forest and scrub located 40 km south west of the source bat population on mainland New Zealand. Bats were monitored using infra-red video cameras, and caught in harp traps during three study periods after release in 2005 (eight weeks in April–June, five weeks in August–September, one week in November–December).
A study in 2006–2008 of four sites in alpine villages in Switzerland (Weinberger et al 2009) found that two of 11 greater horseshoe bats Rhinolophus ferrumequinum and none of seven lesser horseshoe bats Rhinolophus hipposideros remained at release sites in the long term after translocation, 10 bats homed after release and four died with three days of release. Two greater horseshoe bats (one male, one female) translocated 149 km settled in the release area and the female was regularly observed in a new roost in 2007 and 2008, but had an unsuccessful pregnancy in 2007. Two female lesser horseshoe bats remained at release sites 54–57 km away during 10 days of radiotracking, but were not recorded beyond this period. Eight greater horseshoe bats and two lesser horseshoe bats homed after release at sites <20 km from their original roosts. One greater horseshoe bat and three lesser horseshoe bats died of shock or predation within three days of release. Male and female greater horseshoe bats (11) and lesser horseshoe bats (7) of three age classes (adult, 1–2 years and yearlings) were captured from large colonies and translocated to small relict colonies in similar habitats 11–149 km away in May–August 2006. Released bats were monitored with infra-red video and radiotracked for up to 10 days after release. Roosts at release sites were regularly checked in 2007 and 2008.
- Ruffell J. & Parsons S. (2009) Assessment of the short-term success of a translocation of lesser short-tailed bats (Mystacina tuberculata). Endangered Species Research, 8, 33-39
- Weinberger I.C., Bontadina F. & Arlettaz R. (2009) Translocation as a conservation tool to supplement relict bat colonies: a pioneer study with endangered horseshoe bats. Endangered Species Research, 8, 41-48