Mammal recording was introduced to the BBS in 1995 with a view to help improve our knowledge of the distribution and population trends of some of our commoner mammals.
Compared with birds, the population trends of mammals are relatively poorly known. Even though mammal recording has always been a voluntary addition to the scheme, around 90% of BBS squares now hold mammal data.
Download the instructions for monitoring mammals on BBS.
Mammal trends to 2018
BBS count data are used to calculate population trends for nine relatively widespread mammal species, shown below. These trends cover the period 1995–2018.
In 2018, mammal data were recorded on 88% of the 4,022 BBS squares surveyed. In 2,980 squares, live mammals were seen and counted, 425 squares found no evidence of mammals and, on 148 squares, only indirect evidence was seen, such as field signs or via local knowledge.
Of the nine mammals for which trends can be produced from BBS counts, three have increased significantly in the UK as a whole since 1995: Fallow Deer (19%), Roe Deer (80%) and Reeves' Muntjac (140%). Trends for herd mammals, for example, Red and Fallow Deer, should be interpreted with caution. This is because the presence or absence of a herd in a given BBS visit could heavily influence the overall trend for that species.
Two mammals have declined significantly: Rabbit (62%) and Red Fox (42%). The drivers behind these declines are unknown.
More information on the mammals recorded during the 2018 BBS surveys can be seen in the latest BBS Report (pages 28-29).
The information on species detected more often by signs of their presence than by sightings (e.g. Hedgehog, Mole and Badger) can also be used to estimate trends, although these require more careful interpretation.
Brown Hare - East England
Brown Hare - East Midlands
Brown Hare - England
Brown Hare - North West England
Brown Hare - Scotland
Brown Hare - South East England
Brown Hare - South West England
Brown Hare - UK
Brown Hare - West Midlands
Brown Hare - Yorkshire and Humber
Fallow Deer - England
Fallow Deer - UK
Grey Squirrel - East England
Grey Squirrel - East Midlands
Grey Squirrel - England
Grey Squirrel - London
Grey Squirrel - North West England
Grey Squirrel - South East England
Grey Squirrel - South West England
Grey Squirrel - UK
Grey Squirrel - Wales
Grey Squirrel - West Midlands
Grey Squirrel - Yorkshire and Humber
Mountain / Irish Hare - UK
Muntjac Deer - East England
Muntjac Deer - England
Muntjac Deer - South East England
Muntjac Deer - UK
Rabbit - East England
Rabbit - East Midlands
Rabbit - England
Rabbit - North East England
Rabbit - North West England
Rabbit - Northern Ireland
Rabbit - Scotland
Rabbit - South East England
Rabbit - South West England
Rabbit - UK
Rabbit - Wales
Rabbit - West Midlands
Rabbit - Yorkshire and Humber
Red Deer - Scotland
Red Deer - UK
Red Fox - East England
Red Fox - England
Red Fox - South East England
Red Fox - South West England
Red Fox - UK
Roe Deer - England
Roe Deer - Scotland
Roe Deer - South East England
Roe Deer - South West England
Roe Deer - UK
Roe Deer - Yorkshire and Humber
Comparison of BBS mammal trends with the National Gamebag Census
In 2011 the JNCC funded work to compare BBS mammal trends between 1995 and 2009 with another annual scheme: the National Gamebag Census (NGC), carried out by the Game and Wildlife Conservation Trust. The NGC is a voluntary scheme that collects bag statistics from shooting estates, on average about 650 per year. The aim of the project was to produce an overview of trends in abundance and distribution.
Of nine species tested, none differed significantly in their trends between the two schemes. For four species where BBS indicated significant increases between 1995 and 2009, the NCG trend was either not significant (Red Deer, Roe Deer and Reeves’ Muntjac) or alsoshowed a significant increase (Grey Squirrel). Rabbit showed a significant decline on BBS whereas NGC found no significant change.
This work demonstrated the feasibility of producing joint BBS-NGC trends for assessing population change for statutory purposes where a single figure is needed. Results of the spatial mapping were also useful, inshowing areas where species are most often detected and where the most marked changes had occurred. However, due to differences in sampling design and methods, the recommendation is to routinely report temporal and spatial results from the two schemes separately.
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