Information and Advisory Note Number 129 Back to menu
1.1 Scotland and its surrounding seas may support up to
90,000 native species (Usher, 1997); perhaps less than 1% of the world total (Hawksworth
and Kalin-Arroyo, 1995). Scotland's species complement is, nonetheless,
remarkable for its diverse mix of sub-tropical, Atlantic, arctic, arctic-alpine
and boreal elements, many of which are on the extreme edge of their global
range. Some have highly disjunct ranges which otherwise include only a few
widely dispersed localities in Asia, North or tropical America. Thirty Scottish
species occur nowhere else in the world.
1.2 A relatively mild, wet climate is particularly favourable to 'lower' plants.
Consequently, more than half of the liverworts and mosses, and over a third of
the lichens of Europe, occur in Scotland. Being sensitive to air and water
pollutants, many lower plants have their European stronghold along the Atlantic
coast and Western Isles. Also of international importance are Scotland's
breeding populations of seabirds and grey seals, and over-wintering geese.
1.3 Species richness varies markedly across Scotland [Figure 1], Peatlands, for
example, are inherently species-poor, whereas heaths and broadleaved woodlands,
particularly in areas favourable for lower plants, tend to be species-rich.
1.4 Many species have become restricted to modified remnants of their original
habitats. Between the 1940s and 1980s an estimated 17% of semi-natural habitat
in Scotland was converted to more intensive use, such as for farming or forestry
(Mackey et al., 1998).
1.5 The way in which land and wildlife habitats are managed affects the
abundance and diversity of species. For example, changes in farming practices
have been linked to declines in terrestrial bird populations throughout the
United Kingdom in recent decades.
1.6 As part of the UK Government's commitment to the Convention on Biological
Diversity, action plans are being developed for 41 habitats and 226 species
occurring in Scotland. The latter are species that are globally threatened or
rapidly declining in the UK. For each, conservation actions and targets will be
specified with regard to the species' range, population or breeding performance.
Of the 34 species groups represented in the Biodiversity Action Plan, adequate
trend data are generally available for only one; the birds. Hence,
recommendations for monitoring each species' status will also be made.
1.7 An overview of Scotland's BAP Priority Species is given in Action for
Scotland's Biodiversity (Usher et al., 2000).

Figure 1. Variation in species richness in Scotland, based on the distribution
of 3,649 species in 14
taxonomic groups: lichens, seaweeds, bryophytes, stoneworts, rare and scarce
vascular plants,
molluscs, dragonflies and damselflies, grasshoppers and crickets, carabid
beetles, butterflies,
amphibians, reptiles, breeding birds and mammals. Lichens and bryophytes, many
of which have an
affinity for moist, relatively unpolluted areas, form the bulk of the sample
2.1 Species groups for which adequate information is available are summarised in
Table 1. This shows the following.
• Within a sample of rare and endemic vascular plant species examined during
1990-96, the majority appeared to have fewer populations than were known to
exist prior to 1990.
• The distribution of many butterfly species is changing. Most of the species
currently in decline are already scarce, whilst those that are increasing are
already widespread.
• The majority of native freshwater fish species are thought to have declined
recently, having been affected by a wide range of pressures on the quality of
their habitats.
• During the 1970s-90s, population sizes of the majority of wintering waders and
wildfowl (notably the geese), increased markedly1 in abundance. Similarly,
population sizes of the majority of seabird species increased during the
1970s-80s.
• Although the geographic ranges recorded for about half of Scotland's
terrestrial and freshwater bird species showed little change between c. 1970 and
c.1990, almost one-third of species, including 60% of farmland birds, showed a
marked reduction in range size.
• In a survey of widespread, terrestrial and freshwater birds between 1994 and
1998, 16 out of 53 species showed a statistically significant increase in
abundance, five showed a significant decrease and 32 showed no significant
change
• Over one-third of native mammals are thought to be in decline.
• Over one-third of species given legal protection in Scotland, and for which
trend information is available, were thought to be declining in 1997. Almost
half were thought to have shown little recent change.
• The geographic ranges of most non-native plant species introduced into
Scotland are thought to have changed little between the 1950s and 1987-88.
However, of 58 plant species that
increased their range significantly, 31 are thought to have a medium or high
adverse impact on native species.
2.2 No reliable trend data exist for reptiles, amphibians, the majority of
invertebrates or for lower plants.
¹ Here, a 'marked' change is one of 10% or more.
3.1 This profile has been developed using the following key sources, in addition to other references: Atkinson et al. (2000), Lloyd et al. (1991), Fleming (1997), Maitland (1997, 1999), Welch et al. (2001), Butterfly Conservation, Mammal Society, and the Wildfowl and Wetlands Trust. Spatial and other data were provided by the Biological Records Centre, the British Lichen Society and British Trust for Ornithology.
Atkinson, P.W., Austin, G.E., Burton, N.H.K., Musgrove, A.J., Pollitt, M. and
Rehfisch, M.M. (2000). WeBS Alerts 1998/99: Changes in numbers of wintering
waterbirds in the United Kingdom at national, county and Special Protection Area
(SPA) scales. BTO Research Report No. 239. Norfolk: British Trust for
Ornithology.
Fleming, L.V. (1997). Protecting biodiversity: mechanisms and their
effectiveness. In Biodiversity in Scotland: Status, Trends and Initiatives, eds.
L.V. Fleming, A.C. Newton, J.A. Vickery and M.B. Usher. Edinburgh: The
Stationery Office, pp. 261-272.
Hawksworth, D.L. and Kalin-Arroyo, M.T. (1995). Magnitude and distribution of
biodiversity. In Global Biodiversity Assessment, eds. V.H. Heywood, and R.T.
Watson. Cambridge: UNEP.
Lloyd, C, Tasker, M.L. and Partridge, K. (1991). The Status of Seabirds in
Britain and Ireland. London: T&AD Poyser.
Mackey, E.C., Shewry, M.C. and Tudor, G.J. (1998). Land Cover Change: Scotland
from the 1940s to the 1980s. Edinburgh: The Stationery Office.
Maitland, P.S. (1997). Sustainable management for biodiversity: freshwater
fisheries. In Biodiversity in Scotland: Status, Trends and Initiatives, eds.
L.V. Fleming, A.C. Newton, J.A. Vickery and M.B. Usher. Edinburgh: The
Stationery Office, pp. 167— 178.
Maitland, P.S. (1999). Priority freshwater fish in Scotland. A report to SNH.
Haddington: Fish Conservation Centre.
Mammal Society (1999). The State of British Mammals. London: The Mammal Society.
Noble, D.G., Bashford, R.I:, Marchant, J.H., Baillie, S.R. and Gregory, R.D.
(1999). The Breeding Bird Survey 1998. BTO Research Report 225. Thetford:
British Trust for Ornithology.
Usher, M.B. (1997). Scotland's biodiversity: an overview. In Biodiversity in
Scotland: Status, Trends and Initiatives, eds. L.V. Fleming, A.C. Newton, J.A.
Vickery and M.B. Usher. Edinburgh: The Stationery Office, pp. 5-20.
Usher, M.B. (ed.) (2000). Action for Scotland's Biodiversity. Edinburgh: The
Stationery Office.
Welch, D., Carss, D.N., Gornall, J., Manchester, S.J., Marquiss, M., Preston,
CD., Telfer, M.G., Arnold, H.R. and Holbrook, J. (2001). An audit of alien
species in Scotland. SNH Review No. 139. Perth: Scottish Natural Heritage.
Further detailed information on Natural Heritage Trends: Species Diversity can
be found in the following l&A Notes.

To obtain further information about any of the issues raised in this l&A Note,
please contact
Dr Phil Shaw or Ed Mackey
Environmental Audit Group Chief Scientist's Unit
Scottish Natural Heritage
2 Anderson Place
EDINBURGH EH6 5NP
Tel: 0131-446 2464
Fax:0131-446 2405
E-mail: phil.shaw@snh.gov.uk
Table 1. Species trends

