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

Fallow deer © Peter Thompson
The fallow deer went extinct in Britain during the last Ice Age, and was re-established by the Normans for hunting in the 11th century. Typically its coat is fawn with white spotting, but white varieties also occur, as do black ones. The male has palmate antlers cast in April-June. The fallow deer prefers mature broad-leaved or mixed woodlands. Bucks may be shot from 1 August to 30 April, does from 1 November to 31 March.
Further information:
Forestry Commission website
.
Status:
UK: Native
World: Least Concern (IUCN Red List)
Legislation:
Agriculture (Scotland) Act 1948
Wildlife (Northern Ireland) Order 1985
, Schedule 6, 10
Deer (Scotland) Act 1996
Hunting Act 2004
Regulatory Reform (Deer) (England and Wales) Order 2007
© 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
Agriculture Act 1947
Wildlife and Countryside Act 1981
, Schedule 7
Deer Act 1991
Wild Mammals (Protection) Act 1996
Protection of Wild Mammals (Scotland) Act 2002
Animal Welfare Act 2006
Welfare of Animals Act Northern Ireland 2011
Wildlife and Natural Environment (Scotland) Act 2011
Bern Convention
, Appendix III
The fallow deer is widespread across England and Wales, including Anglesey. In Scotland it occurs in isolated pockets, mainly in Perthshire and Stirlingshire, as well as on the islands of Islay, Mull, Lambay and Scarba. It also occurs across much of Ireland, although a scarcity of records means that this is not apparent from the map.
Estimates of fallow deer abundance (numbers of individuals in the spring) across the UK, from Harris et al. (1995):
| United Kingdom | 100,000 |
| England | 95,000 |
| Scotland | 4,000 |
| Wales | 1,000 |
| N Ireland | no estimate |
Index of bag density from
1976 to 2009 (see statistical methods and interpretational considerations).
Error bars represent 95% confidence intervals.
Too few sites provided records to evaluate trends before 1976. After a brief initial increase after 1976, the UK bag index has remained approximately stable between 1982 and 2009. The period of increase corresponded to a period of range expansion that slowed after the 1990s (see maps).
Change in fallow deer 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 | 150 | 1976 | 2009 | 370 -21 to 1051 |
84 -7 to 338 |
30 -23 to 141 |
* significant at P < 0.05
Index of bag density from
1976 to 2009 (see statistical methods and interpretational considerations).
Error bars represent 95% confidence intervals.
Too few sites provided records to evaluate trends before 1976. The bag index for England has remained approximately stable between 1976 and 2009., with perhaps a brief initial increase. Throughout this period there was an expansion in range (see maps).
Change in fallow deer 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 | 127 | 1976 | 2009 | 107 -46 to 507 |
47 -14 to 303 |
21 -31 to 148 |
* significant at P < 0.05
Index of bag density from
1976 to 2009 (see statistical methods and interpretational considerations).
Error bars represent 95% confidence intervals.
Just seven sites reported fallow deer in Scotland between 1961 and 1975. There has been a significant increase in the bag index from 1976 onwards following range expansion and increasing abundance (see maps).
Change in fallow deer 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 |
| Scotland | 18 | 1976 | 2009 | 940* 502 to 3499 |
269 -15 to 1815 |
39* 3 to 787 |
* significant at P < 0.05
There are too few bag records of fallow deer
to produce an index graph.
There are too few bag records of fallow deer 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 fallow deer
to produce an index graph.
There are too few bag records of fallow deer 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 fallow deer 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) | 108 | 1976 | 2009 | 105 -45 to 623 |
48 -10 to 275 |
23 -32 to 141 |
| Westerly lowlands (England/Wales) | 15 | 1995 | 2009 | no data | no data | 20 -64 to 156 |
| 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 fallow deer 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.
The BBS records are limited to England and show no significant change. For all years, the BBS confidence intervals are completely or almost completely within the NGC confidence intervals, indicating good agreement between the two index series.
There are too few bag records of fallow deer to produce a trend starting before 1976.
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).