| Aim and purpose | Although bats constitute over a quarter of British mammalian fauna, they have received little
attention from naturalists, 1 which has resulted in a scarcity of data about these mammals and their populations.
In 1981, the Wildlife and Countryside Act extended protection for wild creatures and plants
and in particular legislated for the comprehensive protection of 15 species of bat. The Act
also coincided with an increased public awareness and interest in their conservation. The
legislation ruled that it was illegal to intentionally kill, injure or take any bat, as well
as damage, destroy or obstruct access to any place used by bats for shelter and protection
or to disturb any bat while roosting. It also made it illegal to sell, hire, barter or
exchange a bat whether alive or dead and keep bats in captivity. 2
One requirement of the Act is that those who wish to rid their house of bats or wish
to carry out works that affect bats or their roosts must first contact the appropriate
government agency responsible for nature conservation to inform it of the proposed action
and allow it time to provide advice. Since 1982, local bat groups, composed of amateur
enthusiasts, have been formed in most counties in Scotland, England and Wales, with the
primary aim of promoting bat conservation. Their major activity has been to visit sites
where bats or their roosts appear to be threatened and either provide on-the-spot
conservation advice or collect information about the problem so that appropriate advice can
be provided by the appropriate government department. This system of site visits in response
to problems has provided a fruitful source of information about bats and their roosts. The
great majority of enquiries received relate to problems with bats in houses or, to a lesser
extent, other buildings, such as churches or factories. Some data is also gathered in
relation to planning development such as road schemes. However only a very small number of
enquiries have been about bats in other roosts, such as trees, mines, caves or bridges. The
data received is therefore heavily biased towards those species found in buildings. A small
amount of information comes from unsolicited visits to buildings to survey for bats, but
this is insignificant compared with that received from enquiries.3
Once advice is sought by the public from a bat group or from one of the three
conservation agencies in England, Scotland and Wales, a volunteer or government employee
visits the site where advice is required. From 1982 onwards all such visitors have been
requested to fill in a form giving details of the problem and the bats or bat roost
involved. These forms are then collected and a summary of the data added to a
computerised database. Visitors are required to identify the species of bat wherever
possible, either from a specimen, from droppings or from other characteristics of the
roost. The method of identification is also noted on the form as some species can be
identified relatively easily, even from droppings, whereas others are more difficult, even
with the specimen in the hand. Other information requested includes name and address of
roost and owner, details about the building and the roost site, description of the problem,
potential threat to the roost, attitude of owners, the extent of usage by bats and the National
Grid Reference of the site. Information gathered by surveyors but not included in the dataset include a
sketch drawing of the roost. Recommendations for action are
also included. Not all the data could easily be handled by the database system, but
essential data about species and location were added in a coded form so that searches for
records of selected species or selected areas could be carried out relatively easily.
It is important to note that as it is a system which depends on the voluntary submission of
records rather than a structured survey methodology, there is no doubt that some interesting
and important data will not have been gathered and that data will be inherently biased.
Species which can be easily identified may be recorded more frequently than others which are
less obvious. The data is biased towards species which frequent buildings. However as well
as collecting data arising from enquiries, information is also collected by the conservation
agencies about bats in underground sites, such as caves and mines, although coverage here is
less complete.4 However to some extent, this data is complementary and for species which use buildings in
the summer and underground sites in the winter the dataset has the potential to
provide very good coverage e.g. the Lesser Horseshoe Bat which uses both buildings and
subterranean sites and is rarely recorded from other types of bat.5
Species of bats protected by the Wildlife and Countryside Act 1981:
|
Common name
|
Latin name
|
| Pipistrelle |
Pipstrellus pipistrellus |
| Nathusius pipistrelle |
Pipstrellus nathusii |
| Brandt's bat |
Myotis brandtii |
| Whiskered bat |
Myotis mystacinus |
| Daubenton's bat |
Myotis daubentoni |
| Natterer's bat |
Myotis nattereri |
| Bechstein's bat |
Myotis bechsteini |
| Brown long-eared |
Plecotus auritus |
| Grey Long-eared |
Plecotus austriacus |
| Noctule |
Nyctalus noctula |
| Leislers bat |
Nyctalus leisleri |
| Serotine |
Eptesicus serotinus |
| Barbastelle |
Barbastella barbastellus |
| Greater Horseshoe bat |
Rhinolophus ferrumequinum |
| Lesser Horseshoe bat |
Rhinolophus hipposideros |
|
|---|