We are delighted to receive feedback on any articles in our magazine, The Geographer. In the Autumn 2013 edition, which was focussed on Forestry, we featured an article on the subject of Deer Management by Mike Daniels. Mike Daniels is Head of Land and Science at the John Muir Trust, you can read his article Deer management : getting out of the rut here.
Member George J. Strachan, who is a retired Principal Teacher of Geography and former keeper/stalker, made the following comments on the article:
"The Autumn issue of ‘The Geographer’ was interesting and well-informed, but the article by Mike Daniels on deer management cannot go unchallenged on a number of points.
On red deer numbers:
The accuracy of the
John Muir Trust (JMT) figures of 150,000 red deer in the 1960s to over 400,000
today are open to dispute. WWF
state 400,000 (Hunt 2003, p.5), but do
refer to a lower figure of 350,000 (Nature, 2004). Putman (2012) gives 360,000 to 400,000 in
2010. G.K. Whitehead believed the NCC’s
1961 total of 155,000 to be an under-estimate.
He arrived at a figure of 188,850 and even considered that an
under-estimate, since his calculations omitted hill sheep farms, common
grazings and grouse moors lying outwith recognised red deer territories (methodology
used is given in detail in Whitehead, 1964).
Even if a higher red deer total in the early 1960s could be
substantiated, the fact remains that the deer population suffered severe
decline as a result of heavy culls by contractors during the War and poaching
post-war when dam construction was on-going in the glens. Only now are deer
numbers probably approaching pre-war levels.
But total figures
conceal regional differences. The SPICe
Briefing on wild deer in Scotland gives red deer counts in selected areas
(Edwards & Kenyon, 2013, table 1).
Wide disparities in % change between the two most recent counts are
apparent. The Monadhliaths, for example,
record a drop of 10% since 2004 to present ; Knoydart 26% down from 1996 to
2003 ; West Sutherland down 14% from 1999 to 2006 to mention but a few. Over the Highlands & Islands the drop
averages 5%. A number rise including an
anomalous increase in South Uist – 884% over a 17 year period from 1983! This figure, if nothing else, backs up the
comment in the WWF report that ‘deer numbers are notoriously difficult to
estimate’ (Hunt, 2003, p.5). Yet of more
importance are local deer densities and carrying capacities. A limited number of areas are pressure points
; environmental damage in the majority of areas across the Highlands is not a
problem.
"Red Deer Stag" by mozzercork is licensed under CC by 2.0 |
On forest and woodland regeneration:
The work of Donald
McVean (Johnston & Balharry, 2001) on regenerating the Coille na Glas
Leitre pinewoods in the Beinn Eighe NNR found that hindrances to regeneration
were far more complex than could be attributed simply to deer browsing. Deep heather prevents the seed from taking
hold, as do bracken and rhododendrons.
The present dislike of muirburn has led to rank heather clothing much of
the Highlands. Woodland regeneration is
prevented and the potential for major moor and forest fires increased. Two years ago, for example, the NTS Torridon
estate suffered a catastrophic fire which swept along Liathach’s south face, a
fire which could have been prevented by a programme of strip burning undertaken
over previous years. Far from being
inimical to forest regeneration, recently burnt ground cover provides the
perfect seedbed for a whole variety of trees.
Judicious burning should be given more consideration by wildlife
organisations. They have a lot to learn
from the old keepers.
Sheep are far more
destructive of woodland habitats than deer.
In the area of South Gairloch red deer seldom came into the oak and
birch woods in any numbers except in periods of extreme winter conditions, e.g.
winters of 1961/62 and 1962/63. On the
other hand sheep grazed them continuously ; over 5000 sheep were hefted on the
Gairloch Conservation Unit (GCU), over three times the number of deer
present. Even the WWF correctly
highlight the need for sheep to be taken into account (Hunt, 2003, p.5). Mountain hares and rabbits also add to the
problem.
Yes, deer browse on
trees. Putman (2012) reckoned that
15-20% of young trees suffered some damage.
This concurs with McVean’s earlier estimate of roughly 25% tree
seedlings destroyed by deer damage (Johnston & Balharry, 2001). This leaves 75% to grow to maturity, surely
sufficient. In areas where planting had
taken place, McVean found that the percentage eaten was much higher. It appears that they smell the freshly turned
earth, hence the need to fence. That is
certainly the case with rabbits and sheep, as any gardener will testify to.
On road accidents involving deer:
This is an emotive
issue used by some organisations as an excuse to get rid of deer. The fact is that, of all deer road casualties
in Scotland during 2003-2005, 1204 (76.9%) involved roe deer and 321 (20.5%) red deer out of a
total of 1566 with sika and fallow accounting for the rest (Langbein, 2007). The problem is that the ‘organisational
finger’ is pointed at red deer with no distinction made as to which deer
species dominates the figures. Generally
where deer do come down on to the road, signs have been erected to warn
motorists. Figures on accidents
involving sheep should be given for comparative purposes. I suspect sheep/vehicle collisions would be
much higher across the Highlands than that of red deer.
On red deer mortalities due to starvation and
exposure:
Frank Fraser Darling’s
(1937) classic study of red deer discovered a 50% mortality rate among red deer
calves. While some was due to predation
by foxes and eagles, most perished over the winter. His figures concurred with those of Cameron
(1923) on the Isle of Jura also at 50%.
Darling (1937) frequently found heavy parasitic infestation in calf
carcases examined. North American
studies on deer have produced similar high calf mortality rates. High deer mortalities are normal and very
seldom related to overgrazing.
Statements such as ‘thousands of deer die every year from starvation and
exposure’ (Daniels, 2013) are misleading and indeed mischievous.
On legislation and close seasons:
Three major pieces of
legislation have been enacted in recent years affecting deer management – the
Deer Scotland Act (1996), the Land Reform Act (2003) and the Wildlife and Natural
Environment (Scotland) Act (2011). All
have retained the close seasons for deer shooting with good reason. They are there for the purposes of preventing
poaching, reducing disturbance of deer particularly during calving time and
ensuring animals are in prime condition when culled. Licences have always been obtainable for
out-of-season culling from the Deer Commission (pre-2010) and the SNH
(post-2010) when necessary. There is no
need to seek changes to the legislation.
On costs to the public purse related to deer
management:
The value of deer
stalking to the UK economy was reckoned at £105m in 2005, of which over 2/3rds
was earned in Scotland. The JMT claim
the costs of deer stalking to the public purse run into tens of millions of
pounds, but when their figures are examined there are inconsistencies. Forestry Commission’s costs for deer fencing
in 2012 was £5,127,452 and grants paid to landowners came to £3,174,200 – not tens
of millions of pounds. Not only that,
the figures given for grants paid includes all participants, not just
landowners (Parliamentary question: S4W-17136).
Similarly, the FCS costs are hedged around by caveats (Parliamentary
question: S4W-17137). Note too that red
deer being seen and heard during the rut must add value to the Scottish tourist trade. As with all businesses, estates pay
considerable taxation annually as do the 2520 stalkers and ancillary staff
employed full-time on the estates.
On deer management groups:
I was personally
involved in the establishment of the first deer management unit in 1967, the
Gairloch Conservation Unit (GCU). Six
estates were affected including the Beinn Eighe NNR and the NTS Torridon
Estate. My own recollection of the GCU
meetings were that they were most amicably conducted and led to annual deer
counts conducted in the Spring. Most DMGs working within the voluntary
principle do a similarly good job.
Statutory measures to bring DMGs into a legally binding framework would
be counter-productive. Essential to the
success of deer management groups is good neighbourliness. If one estate cannot work with the rest, the
result is animosity. Surely the majority
view must prevail ; the others within the deer management group cannot be ruled
one dissenting estate.
In conclusion:
The WANE Act was
passed in 2011 and the whole matter of deer management was fully
discussed. Clearly, a couple of the
members of the Scottish Parliament’s Rural Affairs, Climate Change and
Environment Committee along with the JMT and the RSPB have felt that WANE did
not meet with their agenda. Surely in a
democracy the majority verdict stands."
Cameron
A.G. (1923). The wild deer of Scotland.
Edinburgh.
Clutton-Brock, T.H., Coulson, T. and
Milner, J.M. (2004). Red deer stocks in
the Highlands of Scotland. Nature,
429:261.
Daniels M. (2013). Deer
management : getting out of the rut. The Geographer, Autumn Issue. RSGS.
Darling
F.F. (1937). A herd of red deer. Oxford University Press, corrected 1956.
Edwards T. & Kenyon W. (2013). SPICe Briefing : Wild Deer in Scotland. The Scottish Parliament.
Hunt. J. (2003). Impacts of wild deer in
Scotland – How fares the public interest? Report to WWF Scotland and
RSPB Scotland, Aberfeldy and Edinburgh.
Johnston J.L. & Balharry D. (2001). Beinn Eighe – the mountain above the wood,
SNH publication, Birlinn Ltd.
Langbein J. (2007). Natural deer-vehicle collision project – England 2003-2005.
Highways Agency, Research Report 07/1, data extracted from Table 11A.
Putman R. (2012). Scoping
the economic benefits and costs of wild deer and their management in Scotland. SNH Commissioned Report No. 526
Whitehead G.K.
(1964). The deer of Great Britain and
Ireland, Routledge & Kegan Paul.
George J Strachan
(Retd. PT Geography, Dingwall Academy and former keeper/stalker).
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