Beyond preservation:the challenge of ecological restoration – can you live with ambiguity or do you want to be in charge? A practitioner turned researcher’s tale
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Beyond preservation: the challenge of ecological restoration
1. Beyond preservation:
the challenge of ecological restoration –
can you live with ambiguity or do you want to be in charge?
A practitioner turned researcher’s tale
Adrian Colston
A Dartmoor Blog https://adriancolston.wordpress.com
Twitter: @Dartmoor_AC
Email: ac766@exeter.ac.uk
2. Putting Cambridgeshire in a national wildlife context
0
20000
40000
60000
80000
100000
120000
140000
160000
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39 41 43 45
Hectares
Cambridgeshire 10k ha
Area of nationally important wildlife
habitat (SSSI) per English county
Northamptonshire 2.5k ha
Cumbria 160k ha
Devon 70k ha
3. Protected areas in Cambridgeshire by size
7
27
50
16
10
24
14
2
0
10
20
30
40
50
60
< 1 ha 1-10 ha 10-100 ha >100 ha
Size
Numberbyareaclass
SSSIs
Wildlife
Trust
Reserves
SSSI - average size = 89.5 ha. WT Reserve - average size = 16.4 ha.
Protected areas in Cambridgeshire are very small
4. ‘Nature conservation has
been forced into tiny sites
and many species only
survive as a result of
intensive and expensive
management regimes.’
AC 1997
This is
unsustainable?.
5. • Counties with less than 1/2
the average of nationally
important wildlife habitat
• National conservation
policies and funding have
largely ignored the Black Hole
• No National Parks,
Environmentally Sensitive
Areas, Areas of Outstanding
Natural Beauty, Heritage
Coasts etc.
The Black Hole
BUT lots of people live in the Black Hole and deserve access to a
countryside rich in wildlife
The Black Hole
Colston A (1997) Conserving wildlife in a
black hole Ecos 18: 61-67
6. The original proposition
• The ‘Planned Countryside’ – few areas of high biodiversity
remain so large scale habitat creation is required -> ‘The
Big Idea’
• The ‘Ancient Countryside’ – much of interest remains but it
is fragmented – so here sites should be linked by habitat
creation
• The ‘Highland Zones’ extensive areas of quality exist but
are not always managed well – improve the management
7.
8. Conserving wildlife in a black hole
• Of the 2450 ha of SSSI in Northamptonshire 23%
(560 ha) have been created by humans for
industrial purposes
• Such as quarries, gravel pits, railway cuttings and
reservoirs
• Over 50% of County Wildlife Sites in
Northamptonshire have been created
9. Macgregor N.A., Adams W.M., Hill C.T., Eigenbrod
F. & Osborne P.E. (2012) Large-scale conservation
in Great Britain: taking stock. Ecos 33: 13-23
Progress since 1997
e.g.
Designation of a Special
Protection Area (following
gravel extraction)
Nature Improvement Area
Wildlife Trusts
Futurescapes
‘Putting Wildlife Back on
the Map’
10. Post war Nature Conservation policy in the UK (see NCC 1984, for example) is based upon conserving
pre-modern agricultural landscapes using scientifically researched un-intensive management
prescriptions (Lorimer 2015).
Adams (1997) describes this approach as ‘equilibrium ecology and conservation’, that is, a process
which holds habitats at a single and stable point in their succession.
Such an approach is almost unique to the UK and whilst it has evidently been successful at conserving
many species and habitats, it does make such ecosystems vulnerable when environmental conditions
change as the management prescriptions do not allow them to adapt to the changes (Adams 2003).
Hinchliffe (2006) has described this approach as ‘rendering the present eternal’.
Adams W.M. (1997) Rationalization and conservation: ecology and management of nature in the United Kingdom. Transactions of the Institute of British
Geographers 22: 277-291.
Adams W. M. (2003) When nature won’t stay still: Conservation, equilibrium and control. In Adams and Mulligan (2003 pp220-246)
Adams W.M. & Mulligan M. (2003) Decolonising Nature: strategies for conservation in a post-colonial era. Earth scan. London.
Hinchliffe (2006) Reconstituting nature conservation: towards a carefully political ecology. Geoforum 39: 88-97.
NCC (1984) Nature Conservation in Great Britain. Nature Conservancy Council. Shrewsbury.
12. The Pleistocene Park?
Koniks as Tarpan and Heck Cattle as Aurochsen
Process driven and not target based
Non equilibrium conservation and ecology
13. The ‘Big Idea’ The Great Fen Project A landscape scale aspiration
Buy grade 1 agricultural land so that Woodwalton
Fen and be joined up to Holme Fen
Not process driven - equilibrium conservation
and ecology
Lawton – pre Lawton
14. This is the famous Holne Fen post (photo taken back in 2002). In 1848 a post was driven into the peat
and the top of it was at ground level. The peat has shrunk by around 4 metres over the past 150 years!
15. The RSPB have created new reedbeds from carrot
fields near Lakenheath in Suffolk
Equilibrium conservation and ecology
All the reeds were planted by hand
16. The Future Fen VisionThe National Trust’s Wicken Fen Vision from 800 acres to 15,000 in 100 years
Colston A. (2003) Beyond preservation: the challenge
of ecological restoration. In Adams and Mulligan
(2003).
Hughes F.M.R, Colston A. & Mountford J.O (2005)
Restoring Riparian Ecosystems: The Challenge of
Accommodating Variability and Designing Restoration
Trajectories. Ecology and Society 10(1)
The Wicken Fen Vision (Colston 2003)
is a prominent example of non
equilibrium conservation and ecology
delivering exciting and unexpected
biodiversity outcomes in short periods
of time
An attempt to accommodate variability
via the design of the restoration
trajectories, i.e. it is a non-
deterministic approaches to goal
setting (Hughes et al 2005).
17. Managing water levels
A nature reserve in a plastic bag
The Fen suffers from summer water
shortages. A 2km membrane has been
installed to keep the water in.
Water levels are monitored on a monthly
basis.
The Ancient Fen – 400 acres: equilibrium conservation and ecology
18. Before scrub
removal
After scrub
removal
A better balance
between open
habitats and scrub
Scrub: black
Open habitats: grey
The failure of
equilibrium
conservation and
ecology
When Nature
won’t stay still
19. Managing the Fen for wildlife
The sedge harvest has been carried
out continuously at Wicken since the
1400
Sedge cutting in Wicken
Fen: early morning. Robert
Walker MacBeth 1880s
The harvest in the 1990s
Getting it right: making nature stand still
20. This is a river (called a Lode) which drains the chalk uplands of Cambridgeshire to the south of the
Fens. To the left and right of the river you can see that the ground is much lower.
21. As the ground lowered man-made ditches were required to drain this shrunken landscape
– these ditches were much lower now than the surrounding rivers so the water had to be
pumped into the higher level rivers. This shows one of these drainage ditches – this is
the main one which drains the whole catchment – it is known as the interline.
22. As we saw from the post at Holne Fen the peat was over 4 metres deep. In places now so much
peat has shrunk and been eroded away that the underlying geology is becoming visible. The right
hand side of this field is deep brown and consists of peat – you can however see a patch of
lighter soil running diagonally up the field – this is the underlying chalk now becoming exposed.
23. The report contains this map which shows the current
state of the Fens peat. All the areas that are hatched are
intensively farmed – the Fens are some of our most
productive agricultural soils. However their current
management is clearly not sustainable. The green areas
show where the peat has been seriously degraded and is
becoming incorporated with the underlying soil and the
brown areas show where deep peat soils are still
occurring (but still degrading).
24. The East Anglian Fens – areas in red show where the
peat is still degrading and the areas in green are
where it is not. All the green areas are nature reserves
/ Sites of Special Scientific Interest! The two long
straight green areas are the Ouse and Nene Washes.
This map shows the greenhouse gas emissions that
are occurring today from the peat as a result of the
degradation.
Orange = 4-10 tonnes of CO2 / ha / year
Red = 10-17 tonnes of CO2 / ha / year.
25. Burwell Fen Farm is the area in the middle right of the picture starting at the triangular
pond – this was in 2002 and you can see it is under a crop rotation. You can also see
Adventurer’s Fen, Baker’s Fen and Guinea Hall. These areas were all drained and
ploughed during World War Two as part of the ‘dig for victory’ campaign. They have
subsequently been restored back to wetlands by the National Trust. At the top left of the
picture is the Sedge Fen the 400 acre fragment of the original Fen which escaped
drainage.
26. This is Burwell Fen now – several hundred acres of wetlands created over the past 10 years.
Full of surprises
Blacked-necked grebes, marsh harriers, bittern, stonechat, Cetti’s warbler, short-eared owls, great
white egrets, cranes
The Vision land: non equilibrium conservation and ecology
2,500 acres down 12,500 to go!
Nothing planted – all
natural processes
27. Non equilibrium
conservation and
ecology
Technical advice from
Frans Vera
Nightingales
Turtle doves
Purple emperors
Meat sales
More employment
Designation?
Non equilibrium ->
Equilibrium?
Knepp Wildlands Project
Marren P. (2016) The great rewilding experiment
at Knepp Castle. British Wildlife 27: 333-339.
28.
29. By contrast – Avalon Marshes – equilibrium conservation and ecology
Also full of surprises: from grey heron and bittern to grey heron, bittern, little bittern, little egret, great white
egret, cattle egret, purple heron, night heron and glossy ibis
More
habitat
creation
30. Soft re-wilding (after Kelly 2016) a hybrid between equilibrium and non equilibrium
Encouraging the ‘ineligible features’ – natural flood management and perches for cuckoos!
Kelly M. (2016) Quartz and Feldspar.
Revised edition. Vintage. London.
31. Equilibrium conservation and ecology
does work BUT it does make ecosystems
vulnerable when environmental conditions
change as the management prescriptions
do not allow them to adapt to the changes
32. Atmospheric pollution and the problem with Molinia
Nitrogen, Sulphur, Carbon dioxide , Ozone
When Nature won’t stay still
Equilibrium conservation and ecology – really struggling with this
34. When Nature won’t stay still 2 – wildlife’s problem with climate change
Potential changes in a selection of Dartmoor’s breeding birds
(after Huntley et al 2007)
Current Dartmoor moorland breeding species which the Atlas predicts will find the late
21st century climate envelope unsuitable
Peregrine, Red Grouse, Dunlin, Curlew, Golden Plover, Whinchat, Ring Ouzel, Raven
Current Dartmoor moorland breeding species which the Atlas predicts will find the late
21st century climate envelope still suitable or more suitable
Kestrel, Lapwing, Snipe, Cuckoo, Barn Owl, Skylark, Meadow Pipit*, Stonechat, Nightjar,
Dartford Warbler, Wheatear*, Linnet, Cirl Bunting, Reed Bunting
Species currently not present which may be able to colonise the moors of Dartmoor due
to the changed climate envelope (doesn’t imply that the habitat is suitable though)
Montagu’s Harrier, Hobby, Turtle Dove, Hoopoe, Wryneck, Bluethroat, Cetti’s Warbler,
Red-backed Shrike, Woodchat Shrike, Chough
Huntley et al (2007) A Climatic Atlas of
European Breeding Birds. Lynx Edicions
35. In the face of climate change and atmospheric pollution,
the impacts of which are uncertain and unknown, should
we instead experiment with non-equilibrium ecology and
conservation thereby giving habitats and wildlife an
opportunity to adapt to the changes?
36. But it is not just about wildlife and habitats
It is also about people’s livelihoods and culture
It is also about ecosystem services and in Dartmoor’s case that means peat,
water supply and flood management for example
In the case of the Fenland peat the solutions seem obvious if unpalatable?
But what of Dartmoor’s peat?
Will the current management regime for the moor be the right one in 50 years
time?
Will they conserve the carbon stores and will they encourage carbon
sequestration from the atmosphere?
Short term solutions v long term solutions
Public money for public goods but via what management mechanism?
37. 1. Continuation of the ‘status quo’ (equilibrium
ecology and conservation)
2. Variations of the ‘status quo’ (equilibrium
ecology and conservation)
3. Soft re-wilding - a hybrid equilibrium / non
equilibrium ecology and conservation)
4. Non-deterministic approach to goal setting
which I call constrained re-wilding (non
equilibrium ecology and conservation)
5. Re-wilding (non equilibrium ecology and
conservation) – apex predators and keystone
species
1-3: in control
4-5: ambiguity
The options for ecological restoration
The case for
the defence
Case for the
prosecution