Taxonomy: Class: Mammalia; Order: Artiodactyla; Family: Cervidae

Muntjac © Peter Thompson
The muntjac originates from south-east China and Taiwan, It is a small brown deer with a white underside, no more than 50 cm tall at the shoulder. A characteristic pose is head held lower than the back. It was originally introduced to Woburn Park, Bedfordshire, in 1894. Further releases and escapes have resulted in the species becoming established in the wild since the 1930s. The muntjac likes woodland habitats with a dense understorey, and breeds throughout the year. It can cause serious damage to gardens, coppice woodland and sometimes forestry. The muntjac (both sexes) may be shot all year round.
Further information:
Mammal Society website muntjac
page.
Status:
UK: Non-native
World: Least Concern (IUCN Red List)
Legislation:
Agriculture Act 1947
Deer Act 1991
Hunting Act 2004
Regulatory Reform (Deer) (England and Wales) Order 2007
Muntjac Keeping (Scotland) Order 2011
© Crown Copyright. All rights reserved NERC 100017897 2004
Source
National Biodiversity Network and its data providers who bear no
responsibility for interpretation of the 10x10km grid map
Destructive Imported Animals Act 1932
Wildlife and Countryside Act 1981
, Schedule 7, 9
Wild Mammals (Protection) Act 1996
Animal Welfare Act 2006
Wildlife and Natural Environment (Scotland) Act 2011
Muntjac Keeping (Scotland) Regulations 2011
Bern Convention
, Appendix III
The muntjac is present throughout most of southern and eastern England, and is penetrating into Wales. There are scattered records from northern England and a few from Scotland. It is absent from Ireland.
Estimates of muntjac abundance (numbers of individuals in the spring) across the UK, from Harris et al. (1995):
| United Kingdom | 40,300 |
| England | 40,000 |
| Scotland | 50 |
| Wales | 250 |
| N Ireland | 0 |
Index of bag density from
1980 to 2009 (see statistical methods and interpretational considerations).
Error bars represent 95% confidence intervals.
There has been a rapid increase in the bag index between 1980 and 2009, with average gains of 12% per annum across the period. The increase continued at a similar rate between 1995 and 2009. This reflects the ongoing range expansion and increasing abundance of this introduced species (see maps).
Change in muntjac bags over time, with 95% confidence limits (see statistical methods):
| Country | Sites | Start year |
End year |
Change (%) 1961-2009 |
Change (%) 1984-2009 |
Change (%) 1995-2009 |
| United Kingdom | 176 | 1980 | 2009 | 1756* 387 to 4491 |
1148* 429 to 2904 |
210* 138 to 337 |
* significant at P < 0.05
Index of bag density from
1980 to 2009 (see statistical methods and interpretational considerations).
Error bars represent 95% confidence intervals.
There has been a rapid increase in the bag index between 1980 and 2009, with average gains of 12% per annum across the period. The increase continued at a similar rate between 1995 and 2009. Regionally, the majority of records were from the easterly lowlands, reflecting the source of the ongoing range expansion and increasing abundance of this introduced species (see maps).
Change in muntjac bags over time, with 95% confidence limits (see statistical methods):
| Country | Sites | Start year |
End year |
Change (%) 1961-2009 |
Change (%) 1984-2009 |
Change (%) 1995-2009 |
| England | 176 | 1980 | 2009 | 1760* 387 to 4491 |
1148* 429 to 2904 |
210* 138 to 337 |
* significant at P < 0.05
There are too few bag records of muntjac
to produce an index graph.
There are too few bag records of muntjac to evaluate rates of change over time
| Country | Sites | Start year |
End year |
Change (%) 1961-2009 |
Change (%) 1984-2009 |
Change (%) 1995-2009 |
| Scotland | Too few sites | |||||
There are too few bag records of muntjac
to produce an index graph.
There are too few bag records of muntjac to evaluate rates of change over time
| Country | Sites | Start year |
End year |
Change (%) 1961-2009 |
Change (%) 1984-2009 |
Change (%) 1995-2009 |
| Wales | Too few sites | |||||
There are too few bag records of muntjac
to produce an index graph.
There are too few bag records of muntjac to evaluate rates of change over time
| Country | Sites | Start year |
End year |
Change (%) 1961-2009 |
Change (%) 1984-2009 |
Change (%) 1995-2009 |
| N Ireland | Too few sites | |||||
Change in muntjac bags over time, with 95% confidence limits (see statistical methods):
| Environmental zone | Sites | Start year |
End year |
Change (%) 1961-2009 |
Change (%) 1984-2009 |
Change (%) 1995-2009 |
| Easterly lowlands (England/Wales) | 158 | 1980 | 2009 | 1760* 341 to 4692 |
1150* 388 to 3183 |
209* 138 to 326 |
| Westerly lowlands (England/Wales) | Too few sites | |||||
| Uplands (England/Wales) | Too few sites | |||||
| Lowlands (Scotland) | Too few sites | |||||
| Intermediate uplands/islands (Scotland) | Too few sites | |||||
| True uplands (Scotland) | Too few sites | |||||
* significant at P < 0.05
Since 1995, data on muntjac abundance have been collected under the Breeding Bird Survey (BBS) organised by the British Trust for Ornithology. Below, the UK trend from the NGC is compared to the one from the BBS (from 1995 onwards).
NGC index of bag density (blue) and BBS index of abundance (red), from
1995 to 2009.
Error bars represent 95% confidence intervals.
Like the NGC, the BBS has shown a significant increase since 1995. For all years, the BBS confidence intervals are completely within the NGC confidence intervals, suggesting that both series agree.
There are too few bag records of muntjac to produce a trend starting before 1980.
This report should be cited as: Aebischer,N.J., Davey,P.D. & Kingdon,N.G. (2011). National Gamebag Census: Mammal Trends to 2009. Game & Wildlife Conservation Trust, Fordingbridge (http://www.gwct.org.uk/ngcmammals).