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Coastal soft cliff invertebrates are reliant upon dynamic coastal processes

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Abstract

Coastal soft cliffs in the UK support rich assemblages of invertebrates including species restricted to soft cliffs Howe (Br Wildl 4: 323–331, 2003). Recent analyses have identified a total of 29 species confined to coastal soft cliffs, with a further 78 species having a high degree of dependence (Howe et al. Br Wildl 19: 172–181, 2008). A handful of species once more widespread in the UK, both on the coast and inland, such as the Large Mason Bee Osmia xanthomelana and the Long-horned Bee Eucera longicornis, are now found only or mostly at soft cliff localities. Key habitats include bare sand or glacial till, extensive swards of leguminuous and ruderal plants and hydrological features including seepages, pools and reedbeds. Unhindered dynamic processes such as erosion and cliff failure and unimpeded drainage are critical to soft cliffs retaining their invertebrate interest. By far the richest sites for soft cliff invertebrates are on the Dorset and the Isle of Wight coasts, but other important localities include south Devon, the Llŷn coast in Gwynedd, north Norfolk, Yorkshire and the south Gower coast. The most obvious threats to soft cliff invertebrates are cliff-protection and stabilization schemes and drainage. However, agricultural improvement of cliff-top hinterlands at many sites restricts nesting and foraging activities to the immediate cliff slopes, and acts to fragment and isolate sections of soft cliff. More sympathetic management of these areas is needed to reconnect sites and their associated invertebrate populations, to reduce a dependence upon the cliff slope and to increase the availability of suitable nesting and foraging habitats.

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Acknowledgments

I thank British Wildlife Publishing for allowing the inclusion of material already published in its journal, the National Biodiversity Network and the Bees, Wasps and Ants Recording Society for the use of species distributional data, and Simon Colenutt and Mike Hammett for the use of images.

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Correspondence to M. A. Howe.

Appendices

Appendix 1

Wales Biodiversity Partnership Priority Habitat Mapping. Synopsis for Coastal Soft Cliff (see http://www.biodiversitywales.org.uk/en-GB/Coastal).

Coastal soft cliffs are a significant but highly localised component of the Welsh coast, their total length of c.100 km comprising less than 7 % of the coastline (Howe 2003). As well as their geomorphological importance and significance in terms of coastal processes, Welsh soft cliffs also support invertebrate species and faunas of national importance. These are associated with areas of bare ground and pioneer and ruderal plant communities promoted by regular landslips, and with seepages, pools and other hydrological features. Recent studies (Howe 2002, 2003: Howe et al. 2008) have identified 29 species of insect (Grade 1 species) in the UK that are confined to coastal soft cliffs and a further 78 species (Grade 2 & 3) with a strong affinity to the habitat. Key soft-cliff sites in Wales, which rank as among the top sites in the UK, include:

North Llŷn Soft Cliffs

12.4 km of predominantly northwest facing, slumping cliffs from Porth Oer to Gwydir Bay and including Porth Dinllaen, Porth Nefyn and Porth Pistyll. Cliffs of glacial till, sands and gravels support extensive leguminous swards and numerous springs and seepages, with some fen and localised stands of common reed. The area supports 17 soft cliff species including Sitona gemellatus and Symplecta chosenensis.

South Llŷn Soft Cliffs

14 km of predominantly south-facing, eroding cliffs from Aberdaron Bay to Criccieth and including Porth Ceiriad, Porth Neigwl and Porth Ysgo. Cliffs of glacial till and sand support extensive leguminous swards and numerous springs, seepages, pools and fen with localised stands of common reed. The area supports 23 soft cliff species including Osmia xanthomelana, Symplecta chosenensis and Tachys micros.

South Ceredigion Soft Cliffs

1.2 km of west-facing steep, vegetated cliffs of glacial till and sands & gravels at Creigiau Gwbert and Traeth y Mwnt with numerous springs and seepages and areas of bare ground. The area supports 16 soft cliff species including Symplecta chosenensis.

Castlemartin Peninsula Soft Cliffs

1.25 km of southwest and west-facing eroding cliffs at Great & Little Furzenip, Freshwater East, Swanlake & Manorbier Bay. Cliffs comprise head and blown sand with some base-rich seepages, and deposits of clays and gravels overlying Old Red Sandstone, with springs and seepages and small stands of common reed. The area supports 13 soft cliff species.

South-West Gower Coast

8.6 km of predominantly south-facing, sparsely vegetated low cliffs, from Worms Head to Oxwich Point, of dry, eroding head overlying Carboniferous limestone with headlands of limestone grassland and heath. Includes The Sands, Horton Cliffs, Overton Cliffs & Mere, Fall Bay & Rhossili Bay. The area supports 20 soft-cliff species.

Whilst many English coastal soft cliff sites have been the focus of engineering projects to prevent erosion, the main threats in Wales are the loss of headlands to agricultural improvement, alterations to natural drainage patterns, and fertiliser and pesticide run-off. Such activities disrupt natural erosion patterns, restrict less mobile species to the immediate cliff face and reduce connectivity between soft-cliff sites, lead to the loss of seepages, pools and fen vegetation, and encourage the growth of coarse grasses to the detriment of pioneer swards and bare ground.

Actions required

Restoration of semi-natural vegetation on cliff tops to provide additional areas of flower- rich habitats and increased connectivity between soft-cliff sites;

Restoration of natural drainage patterns to recreate dynamic coastal processes and enhance hydrological features;

Prevention of fertiliser and pesticide run-off onto cliff faces to promote bare ground and early-successional swards;

Establishment of grazing appropriate to the requirements of soft-cliff habitats and species;

Prevention of improvement and upgrading to track surfaces with aggregate;

Integration of coastal access and habitat management to ensure that people’s enjoyment of the “wild” nature of this stretch of coast is enhanced without impacting on habitats and species. It is of particular importance to address concerns regarding stock management and access to avoid coastal abandonment.

Priority sites for action

Coastal soft-cliff sites are given priority rankings of A, B and C. The accompanying maps show Priority A sites which should be the major focus of action. Priority B and C sites will be included within wider biodiversity mapping work with management of B and C sites being undertaken when opportunities arise.

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Howe, M.A. Coastal soft cliff invertebrates are reliant upon dynamic coastal processes. J Coast Conserv 19, 809–820 (2015). https://doi.org/10.1007/s11852-015-0374-z

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