Sites of Special Scientific Interest (SSSIs) in Kent, England. In England the body responsible for designating SSSIs is Natural England, which chooses a site because of its fauna, flora, geological or physiographical features. As of 2008, there are 98 sites designated in this Area of Search, of which 67 have been designated due to their biological interest, 21 due to their geological interest and 10 for both.
The links to maps for some of the Sites of Special Scientific Interest in Kent are below.
The coastline from Dover harbour to Kingsdown is of extreme importance geologically and physiographically, and for its varied floral and faunal communities which include many rare species.
The invertebrate fauna of the site is rich, including important communities of Lepidoptera (moths and butterflies) and Coleoptera (beetles). Locally-restricted species found here include the adonis blue butterfly Lysandra bellargus, the scarlet tiger moth Callimorpha dominula, a ground-beetle Bradycellus distinctus, and some rare weevils of the family Apionidae. There are numerous breeding sea birds along the cliffs including fulmars, rock pipits and lesser-black backed gulls; kittiwakes have been established since 1967, their expanding population now exceeds 1100 pairs, but are still found nowhere else in Kent. The South Foreland valley at St Margarets is a significant landfall for migrant birds in the spring and a gathering point for dispersal in the autumn. More importantly many migrants breed here including whitethroat, blackcap, grasshopper and other rarer warblers. Old wartime fortification-systems, of which there are several within the site, attract black redstarts. Near Kingsdown is one of the two cliff-nesting colonies of house martins in Kent. In addition the site includes important chalk foreshore habitats, particularly those at St Margarets Bay. These support the most species-rich littoral chalk algal flora in south-east England. The wide wave-abrasion platform at the foot of the cliffs provides a diverse range of rock formations and habitats colonised by rich and complex seaweed communities, the lower shore red algae being particularly luxuriant. Examples of algae characteristic of lower salinities are present where freshwater springs emerge on the shore, and the cliff face supports well developed examples of the unusual algal communities characteristic of this habitat, exhibiting clear vertical zonation patterns.
Dungeness, Romney Marsh and Rye Bay is a nationally important site by reason of a diverse range of biological and geological features, specifically the coastal geomorphology of Dungeness and Rye Harbour and the following nationally important habitats: saltmarsh, sand dunes, vegetated shingle, saline lagoons, standing waters, lowland ditch systems, and basin fens. These habitats and others within the site support the following nationally important species interests: populations of four vascular plant species listed in Schedule 8 of the Wildlife and Countryside Act 1981 (as amended); an assemblage of Schedule 8, nationally rare and nationally scarce vascular plants; populations of the vulnerable Warne’s thread-moss Bryum warneum; populations of water voles Arvicola terrestris; an assemblage of breeding birds associated with shingle beaches and saltmarsh, lowland damp grasslands, lowland open waters and their margins, and scrub; breeding numbers of 16 species of bird; assemblage of over 20,000 waterfowl in the non-breeding season; wintering numbers of 17 species of bird and three species during passage periods; metapopulations of great crested newts Triturus cristatus; endemic species and subspecies of invertebrates; populations of two invertebrate species listed in Schedule 5 of the Wildlife and Countryside Act 1981 (as amended); populations of ten endangered, vulnerable and rare invertebrate species; assemblages of invertebrates occurring on ‘dry’ coastal habitats; and assemblages of wetland invertebrates.
Dungeness, Romney Marsh and Rye Bay is a nationally important site with a diverse coastal landscape comprising a number of habitats which appear to be unrelated to each other. However, all of them exist today because coastal processes have formed and continue to shape a barrier of extensive shingle beaches and sand dunes across an area of intertidal mud and sand flats. The site contains the largest and most diverse area of shingle beach in Britain, with low lying hollows in the shingle providing nationally important saline lagoons, natural freshwater pits and basin fens. Rivers draining the Weald to the north were diverted by the barrier beaches, creating a sheltered saltmarsh and mudflat environment, which was gradually in-filled by sedimentation, and then reclaimed on a piecemeal basis by man. Today this area still contains relict areas of saltmarsh (the largest areas of this habitat in East Sussex) and an extensive network of ditches which drain areas of grazing marsh, arable farmland and reedbed. Human activities have further modified the site, resulting in the creation of extensive areas of wetland habitat due to gravel extraction. This highly unusual coastal landscape has varied soils and shingle deposits which help to explain the way in which Romney Marsh and Rye Bay were formed, and may evolve in the future.
Interpretation of the coastal and environmental changes at the site relies heavily on the relationship of the shingle ridges and associated deposits. The lateral and vertical variations in the deposits, and the ability to correlate and date the backwater and shingle ridge sequences is a key factor in furthering our understanding of the foreland development. The continuing evolution of the foreland is itself of interest. The site is responding to a variety of influences including reduction in sediment supply, coastal defence works, recycling for beach management, training walls at Rye Harbour and sea-level rise, including that caused by climate change. However, despite these influences the site continues to evolve, and understanding the ongoing evolution, including comparison to historical changes and the influence of human activity, is a key element of the interest. In this context the site is one of a suite of five south-west facing beach systems along the coast of the English Channel which all show contrasting characteristics in relation to sediment supply, erosion and orientation to the dominant wave direction.
Downstream of the Monk Bretton Bridge in Rye, the site supports higher saltmarsh communities on raised areas adjacent to the river, dominated by common saltmarsh-grass Puccinellia maritima and, where the saltmarsh is grazed, red fescue Festuca rubra. The nationally scarce sea-heath Frankenia laevis occurs in parts of the upper saltmarsh. Low-mid marsh communities of common saltmarsh- grass and sea-purslane Atriplex portulacoides, with sea wormwood Seriphidium maritimum and sea aster Aster tripolium, occupy the inner areas of the marsh. In the immediate vicinity of Rye Harbour, there is a pure stand of sea-purslane. The Rother upstream of the bridge is canalised and there are only narrow strips of saltmarsh habitat along the flood banks. These areas are characterised by the low-mid marsh sea-purslane saltmarsh community, although the sea couch Elytrigia atherica drift line community is also represented.
The site includes three sand dune systems at Camber, Romney Warren and Greatstone, representing different structural types of sand dune and sand dune formation associated with the shingle structures of Dungeness and Rye Harbour. Camber Sands is a ness/cuspate foreland dune system that has developed over a series of shingle ridges radiating from its eastern end. The system supports a typical successional sequence of dune habitats. The foredune vegetation contains a classic sequence of sand couch Elytrigia juncea dune and marram Ammophila arenaria dune with sand couch and red fescue Festuca rubra. The foredune also supports sea buckthorn Hippophae rhamnoides scrub, although some of this has been planted as a stabilisation measure. Further from the sea, the semi-fixed marram vegetation leads into fixed dune grassland. Locally this includes small patches of more lichen-rich open dune vegetation. In areas with a taller sward there is a tendency for mesotrophic (moderate nutrient status) grassland to develop with sea couch Elytrigia atherica and, on the higher ground, marram.
are a narrow bay dune system and consist largely of a successional sequence of dune habitats from foredune to mobile dune and dune scrub habitats. An important feature of these dunes is the transitions they demonstrate between vegetated shingle beach and foredune communities. For some of their length the dunes are also fronted by a strandline community. The foredunes support a narrow and discontinuous band of sand couch fronting marram-dominated mobile dunes, which make up the majority of the dune system. There are also areas of sea buckthorn scrub. Where the dunes are broader towards the north of the site, the mobile dunes grade into areas of semi-fixed dune and fixed dune grassland. Romney Warren is a stable ness/cuspate foreland dune system developed over a series of ancient shingle ridges. There are two main types of fixed dune grassland communities. Grasslands in the south and south-east are dominated by mixtures of red fescue, common bent Agrostis capillaris, sea couch, smooth meadow-grass Poa pratensis, crested hair-grass Koeleria macrantha and sand sedge Carex arenaria. In contrast, the northern end supports dense species-poor swards dominated by sand sedge and sheep’s fescue Festuca ovina, developed over acidic sands. In the south-west, dense mesotrophic grassland has developed over richer soils. This is dominated by false oat-grass Arrhenatherum elatius and sea couch, with cock’s-foot Dactylis glomerata and red fescue.
Lydd Ranges supports the only known example of a “holly Ilex aquifolium wood” on shingle. Around the landward edge of the shingle beaches (such as at the northern end of Lydd Ranges) there are relict areas of sandy shingle which probably represent old dune systems. Even the areas of apparently bare shingle are in fact ‘vegetated’ by encrusting lichens, including the near-threatened species Rinodina aspersa. On naturally bare shingle ridges near the coast at Rye Harbour, soil development is limited and only a few specialised pioneer plant species can colonise, such as sea-kale Crambe maritima, sea pea Lathyrus japonicus ssp. maritimus, sea campion Silene uniflora and curled dock Rumex crispus. As finer material accumulates within the gravel matrix, more species become established including viper’s-bugloss Echium vulgare, yellow horned-poppy Glaucium flavum and herb-robert Geranium robertianum ssp. maritimum. After several centuries, a thin, well-drained soil develops on the older shingle ridges and a variety of grassland species occur, including buck’s-horn plantain Plantago coronopus, common stork’s-bill Erodium cicutarium, sand spurrey Spergularia rubra, the vulnerable smooth cat’s-ear Hypochaeris glabra and some fifteen species of vetch and clover. Around Camber Castle there are unique ancient ridges that have an extremely specialised grass flora. Where the shingle has been disturbed or removed in the past to a level above the water table there is a succession of different species to those found elsewhere. Here, species such as Danish scurvygrass Cochlearia danica, common bird’s-foot-trefoil Lotus corniculatus, rue-leaved saxifrage Saxifraga tridactylites and the endangered least lettuce Lactuca saligna occur. Natural shingle wetlands: saline lagoons, standing waters and basin fens The vast shingle beach at Dungeness contains a number of natural wetlands (unlike the extensive flooded pits created by gravel extraction), referred to as the Open and Fossil Pits, within Dungeness RSPB Reserve and Lydd Ranges. These wetlands have been subject to colonisation by vegetation and (the Open Pits at least) display stages of a classic hydroseral succession, from open water and marginal reed-swamp, through a form of marsh or fen, to grey willow Salix cinerea carr. Some of the pits have reached a stage in the hydroseral succession where they have little or no open water. Most have floating rafts of vegetation, varying in the degree to which they have stabilised. These floating rafts of vegetation are typical of the “Schwingmoor” type of basin fen, where layers of peat are separated by lenses of water. The pits contain a range of fen types from nutrient-rich to poor fen, with vegetation ranging from single species swamps to more complex communities. Much of the vegetation comprises common reed swamp but poor fen communities are dominated by tall-herb fen, with marsh cinquefoil Potentilla palustris, the nationally scarce marsh fern Thelypteris palustris, common cottongrass Eriophorum angustifolium and bottle sedge Carex rostrata. Some pits have hummocks of bog-moss, including blunt-leaved bog-moss Sphagnum palustre and spiky bog-moss S. squarrosum, and one pit contains a small stand of great fen-sedge Cladium mariscus. The oldest of the pits are now on the eroding south coast of Dungeness (in Lydd Ranges) and have reverted to saline conditions. They are typical, relatively stable, shingle percolation lagoons. The fauna of the pools that lie seaward of the embankment is comparatively diverse and includes the lagoonal specialist mud-snail Ventrosia ventrosa. The maritime influence of these pools is shown by the presence of the bivalve mollusc Abra tenuis and the polychaete worm Capitella capitata. The remaining pools lie landward of the embankment. They are surrounded by grassland with sea- purslane and sea aster, and have a dense submerged flora of tasselweed Ruppia spp. The tasselweed is well colonised by Ventrosia ventrosa, whilst the benthos predominantly comprises oligochaetes and opportunistic insects, but ragworms Nereis diversicolor are also common. The lagoons demonstrate a range of salinities and all show landward transitions to vegetated shingle habitats and to the shingle ridge geomorphology of Dungeness.
The Dowels contains the greatest proportion of freshwater ditches on Walland Marsh and has the highest plant species diversity, with the nationally rare sharp-leaved pondweed Potamogeton acutifolius and several nationally scarce species, including greater water-parsnip Sium latifolium and marsh-mallow Althaea officinalis. Although components of this diverse flora are also found in the adjacent northern end of Snargate, the majority of Snargate is similar to Fairfield, Woolpack and Cheyne Court, where most of the ditches contain a characteristic but less diverse brackish community. The typical aquatic species are soft hornwort Ceratophyllum submersum, spiked water-milfoil Myriophyllum spicatum, fennel pondweed Potamogeton pectinatus, brackish water- crowfoot Ranunculus baudotii, thread-leaved water-crowfoot R. trichophyllus and horned pondweed Zannichellia palustris. The dominant emergent species in these areas are sea club-rush Bolboschoenus maritimus, common reed and lesser bulrush Typha angustifolia. The ditch banks support a number of upper saltmarsh species, such as saltmarsh rush Juncus gerardii, sea-milkwort Glaux maritima and sea arrowgrass Triglochin maritimum. The large area of grazing marsh at East Guldeford also contains predominantly brackish ditches, although overall it is less brackish than Snargate, Fairfield and Woolpack. The ditch banks which are ungrazed or only lightly grazed are particularly important for marsh-mallow. The grazing marsh ditches on Pett Level range from freshwater to brackish, and this contributes to the diversity of the fauna and flora. Recently cleared ditches rapidly become invaded by aquatic plants, such as fennel pondweed, soft hornwort and bladderwort Utricularia australis in the brackish ditches, and rigid hornwort Ceratophyllum demersum, broad-leaved pondweed Potamogeton natans and hairlike pondweed P. trichoides in those with a freshwater influence. The brackish ditches eventually become invaded by emergent species such as sea club-rush and grey club-rush Schoenoplectus tabernaemontani, while arrowhead, lesser bulrush, greater pond-sedge Carex riparia, and water dock Rumex hydrolapathum are more common in the freshwater ditches. Eventually, the late succession ditches become dominated by common reed.
The site supports populations of four plant species that are listed in Schedule 8 of the Wildlife and Countryside Act 1981 (as amended): Jersey cudweed Gnaphalium luteoalbum grows on the margins of gravel pits in Dungeness RSPB Reserve; least lettuce occurs in vegetated shingle at Rye Harbour Local Nature Reserve (LNR); there is a small colony of the early spider-orchid Ophrys sphegodes growing on an area of disturbed shingle adjacent to the nuclear power stations at Dungeness; and there are colonies of lizard orchids Himantoglossum hircinum (further details about the locations of these colonies are confidential due to the threat posed by illegal plant collectors). The extensive areas of natural and semi-natural habitats, including shingle beaches, sand dunes, saltmarsh, grazing marsh, waterbodies and fens, support a large assemblage of nationally rare and nationally scarce vascular plant species (including the four Schedule 8 species listed above). Foremost amongst this assemblage are the suites of species associated with shingle beaches, grazing marsh and saltmarsh (including brackish wetlands in the shingle beaches and brackish ditches). The shingle beaches of Dungeness and Rye Harbour support at least six nationally scarce species (in addition to least lettuce and early spider-orchid), including the critically endangered red hemp-nettle Galeopsis angustifolia, and the near-threatened Nottingham catch-fly Silene nutans and yellow- vetch Vicia lutea. Saltmarshes and other brackish wetlands are equally rich, with at least eight nationally scarce species, including the vulnerable sea barley Hordeum marinum and Borrer’s saltmarsh-grass Puccinellia fasciculata, and the near-threatened sea-heath.
especially the extensive ditch systems of Walland Marsh, Denge Marsh and Pett Level, support the nationally rare (and critically endangered) sharp-leaved pondweed and at least six nationally scarce species, including the endangered greater water-parsnip, and the vulnerable divided sedge Carex divisa and rootless duckweed Wolffia arrhiza. The vulnerable Warne’s thread-moss Bryum warneum is a colonist of unshaded calcareous sand that must be persistently damp all year but not inundated by standing water. Warne’s thread-moss occurs on wet sand beside a large freshwater gravel pit in Dungeness RSPB Reserve. Several smaller satellite colonies have become established beside small pools to the north of the main colony.
The extensive network of grazing marsh ditches, some in association with areas of wet reedbed, provides habitat for large populations of water voles Arvicola terrestris. The SSSI contains the core areas of an extensive distribution of this species in the Romney Marsh and Rye Bay area. The densest and most persistent population occurs at the southern end of Walland Marsh, between East Guldeford and Jury’s Gap. Water voles also occur in large numbers further north on Walland Marsh at Woolpack, Fairfield and The Dowels, as well as in Rye Harbour LNR and on Pett Level. The population fluctuates in numbers and range, largely dependent on summer water levels. The area is particularly favourable for water voles because many of the ditches hold water in the summer, stretches of ungrazed ditch bank provide vegetation cover, and predatory mink Mustela vison occur at a low density.
The extensive areas of open water, grazing marsh, reedbed and intertidal habitat in the SSSI provide safe feeding and roosting sites for nationally important numbers of waterfowl, together regularly supporting in excess of 20,000 individuals of more than 60 species. As well as the waterbird species listed below, which individually occur in nationally important numbers (exceeding 1% of the Great Britain populations), this assemblage regularly includes large numbers (greater than 12,000 individuals) of lapwing Vanellus vanellus. Sixteen species of waterfowl regularly winter here in nationally important numbers: mute swan Cygnus olor, Bewick’s swan C. columbianus bewickii, European white-fronted goose Anser albifrons albifrons, wigeon Anas penelope, gadwall A. strepera, teal A. crecca, shoveler A. clypeata, pochard Aythya ferina, little grebe Tachybaptus ruficollis, great crested grebe Podiceps cristatus, cormorant Phalacrocorax carbo, bittern Botaurus stellaris, coot Fulica atra, golden plover Pluvialis apricaria, ruff Philomachus pugnax and sanderling Calidris alba. Two species of waterfowl regularly occur in nationally important numbers during migration periods: whimbrel Numenius phaeopus in spring and common sandpiper Actitis hypoleucos in autumn. The SSSI also supports nationally important numbers of hen harrier Circus cyaneus in winter and aquatic warbler Acrocephalus paludicola on autumn passage.
The particular combination and distribution of aquatic and terrestrial habitats in the SSSI provide exceptional breeding, foraging and hibernation conditions for great crested newts Triturus cristatus. The SSSI supports three metapopulations: one centred on Lydd Ranges; one extending from Dungeness RSPB Reserve to Lydd Airport; and one at Romney Warren. The newts depend on water for breeding, which takes place in spring, and particularly favour moderately deep, well- vegetated pools without fish. During the first two or three years of life before breeding starts, and outside the breeding season, great crested newts are dependent on terrestrial habitats to provide foraging areas and places to hibernate. The habitats which occur around and between the waterbodies are therefore as important as the presence of suitable breeding ponds.
The site contains one of the most Important localities for marine interest between the Isle of Wight and Flamborough Head, by virtue of the combination of intertidal habitats and communities, another rare species which are present. Also of considerable interest are the plant and animal communities of the adjoining sublittoral zone.
The Gault and Lower Greensand cliffs at the western end of the site are unstable and sparsely vegetated. In the Warren, landslips have given rise to a succession of steep, broken slopes where scrub and woodland is developing and there are several small ponds. The combination of southerly aspect, chalk substratum and maritime influence of the site provides favourable conditions for a wide diversity of invertebrate species, several of which occur sparsely if at all outside south east England. These include the harvestman Trogulus tricarinatus and the millipede Polydesmus testaceus. A number of rare Lepidoptera species have bred within the site including the fiery clearwing moth Bembecia chrysidiformis, known only from Folkestone Warren in Britain. Regular migrants to the site from the continent include the sub-angled wave moth Scopula nigropunctata. The ornithological interest of the site includes cliff-nesting and wintering bird species and migrants, particularly passerines such as chats and warblers in the autumn, which make landfall in Folkestone Warren and in other areas of scrub. The site contains one of the two cliff-nesting colonies of housemartins in the county and fulmars breed on the cliffs in reasonable numbers for Kent. Small numbers of purple sandpiper overwinter on the rocky foreshore at Copt Point and below Shakespeare Cliff.
The range of geological substrata exposed on the shore provides a diversity of intertidal habitats and these are colonised by a wide variety of marine plants and animals in characteristic assemblages. Many species found here are rare in south east England or nationally and reach their eastern limit of distribution in the Eastern Channel at this site. The chalk shore at Abbots Cliff and Shakespeare Cliff are among the better examples of their type in south east England. They possess full vertical shore zonations and a wide range of plant and animal assemblages characteristic of this soft rock are present on the wave cut platform and chalk boulder habitats, the latter being continually renewed from the unprotected cliff face. The wave exposed headland at Abbots Cliff Is animal dominated in contrast to the Shakespeare Cliff site with its luxuriant algal growths. The clay bands of the Lower Chalk form wave cut intertidal platforms between Shakespeare Cliff and Abbots Cliff, and in East Wear Bay These clays support characteristic and unusual assemblages of small algal species with many ephemerals and including rarities such as Scinaia forcellata, Sphacellana spp and Derbesia tenuissima, and species well outside their normal limits of distribution, such as Chorda filum. Copt Point, formed principally of hard Lower Greensand, is a unique site in Kent and south east England. It supports algal assemblages more typical of northern and western England including the fucoid algae Pelvetia canaliculata and Ascophyllum nodosum, which are very rare on natural substrata in the south east. The intertidal fauna are a so unusual for south east England, beingparticularly species-rich and with some species rarely recorded east of the Isle of Wight.
Whilst the SSSI boundary follows Mean Low Water Mark, there are also marine communities of interest on the lower shore and in the sublittoral which itself falls into three fairly distinct regions. Off Copt Point Folkestone, the sea-bed is rocky (greensand), but the presence of the sewage outfall has resulted in much of the area becoming dominated by extensive mats of mussels, upon which are feeding large numbers of starfish Species diversity here is low, although potentially could be high in East Wear Bat the sea bed in the shallow sublittoral is predominantly sandy, and supports polychaete worms, bivalve molluscs and many juvenile flat fish. The most interesting area is off Abbot’s Cliff and Shakespeare Cliff where there is an almost continuous belt stretching to around 300 m offshore which consists of chalk bedrock overlain with chalk boulders up to 2m high. In places, clay and marl bands in the Lower Chalk are exposed, so providing a variety of different substrata for the flora and fauna There are rich growths of algae, including kelps, and animal ‘turf’, together with a range of larger animals. The sublittoral chalk habitat is scarce in Kent, and the site may mark the eastern limit of distribution along the English Channel of species such as the kelp Laminaria nyperborea.
This site lies along the flood plain of the River Medway, which at this point is still tidal. A variety of habitats are present including extensive reedbeds, open water, fen, grassland, scrub and woodland. The many different habitats support a wide variety of breeding birds and the site is also important for wintering wildfowl and waders. A number of scarce wetland plants occur and it is also a locality of a rare moth, a rare beetle, and 3 rare bee species.
The extensive reedbeds, subject to occasional tidal flooding, are dominated by common reed Phragmites australis. Scarce plants include marsh sow-thistle Sonchus palustris and marsh mallow Althaea officinalis; the latter is the larval an o e nationally rare marsh-mallow moth Hydraecia osseota which is also found here. Many typical reedbed birds breed in areas including reed warbler Acrocephalus scirpaceus, water rail Rallus aquaticus and occasionally bearded tit Panarus biarmicus. In addition large flocks of swallows Hirundo rustica, and sand martins Riparia riparia roost in the reed beds in autumn together with wagtails Motacilla species which remain for the winter.
The diversity of habitats supports many interesting invertebrates, including a good representation of characteristic wetland species and a significant number of nationally scarce species together with 5 nationally rare species including the marsh-mallow moth and rove beetle Stenus calcaratus and the blue carpenter bee Ceratina cyanea. Standing water frequently collects on the pasture during wet weather and attracts many birds. Lapwing Vanellus vanellus and redshank Tringa totanus regularly breed in these areas and in winter many wildfowl and waders gather including teal Anas crecca, shelduck Tadorna tadorna and snipe Gallinago gallinago. Woodland and scrub There are several areas of dense scrub within the site consisting mainly of hawthorn Crataegus monogyna, blackthornPrunus spinosa with alder Alnus glutinosa in the wetter areas. At the southern end, surrounding a large reedbed is a damp woodland of alder and crack willow Salix fragilis with some ash Fraxinus excelsior and oak Quercus robur on drier ground. The ground flora, particularly in the wetter areas resembles that of the adjacent reedbed with a predominance of common reed in places. Yellow flag Iris pseudacorus, great horsetail Equisetum telmateia and hemlock water- dropwort Oenanthe crocata also occur. Typical woodland birds such as tree creeper Certhia familiaris and great spotted woodpecker Dendropus major breed. Many other birds breed both in the wood and the patches of scrub, including nightingale Lucinia megarhynchosand on occasions the rare cetti’s warbler Cettia cetti.
Ash-maple coppice is the predominant woodland type on the slopes of this dry chalk valley. This grades into beech high forest on the thin calcareous soils of the upper slopes with hornbeam coppice on the deeper soils in the valley bottom. The varied ground flora includes a number of uncommon plants. The wood also supports many breeding birds. The ash-maple woodland has a varied coppice layer under pedunculate oak standards. While ash and hazel are the most common coppiced species, field maple, birch, sweet chestnut and wild cherry are also present and hawthorn is a common shrub. In the valley bottom the coppice is more uniform. Hornbeam and hazel are the predominant coppiced species with occasional ash and field maple and a few oak standards. The high forest on the upper slopes is dominated by mature beech with some oak. The shrub layer under the beech is sparse in heavily shaded areas but elsewhere, especially along the woodland edge, there is a variety of species including wild privet, spindle and wayfaring tree; shrubs characteristic of chalk soils.
Much of the coppice has not been cut recently and consequently the ground flora is poor. Bramble Rubus fruticosus, bluebell Hyacinthoides non-scripta, dog’s mercury Mercurialis perennis and wood anemone Anemone nemorosa are the most abundant plants. The flora is more varied in the recently cut coppice, and includes wood spurge Euphorbia amygdaloides and caper spurge E. lathyrus.
Moschatel Adoxa moschatellina and lesser celandine Ranunculus ficaria grow in the wetter areas in the valley bottom. Beneath the beech high forest the flora is diverse except where there is heavy shade. Sanicle Sanicula europaea, sweet woodruff Galium odoratum and wood melick Melica uniflora occur with a number of orchids; bird’s-nest Neottia nidus-avis, fly Ophrys insectifera and lady Orchis purpurea. The latter is a scarce species restricted in Britain to Kent and is characteristic of Kentish woods on chalk soils. A variety of woodland birds breed, including tree pipit, nuthatch, hawfinch and several tits and warblers.
Situated to the south-east of Sevenoaks, this site comprises an extensive area of woodland of varied composition on the Lower Greensand. Some plants and invertebrates of restricted distribution are present, including the slug Tandonia rustica at its only known British locality. On the plateau, in the north of the site, the Lower Greensand is overlain by angular chert drift giving rise to acidic soils. To the south there is a steep scarp slope where the exposed ragstone (a calcareous sandstone) has resulted in contrasting soils of more base-rich status. These varying soil types are reflected in the woodland composition. Much of the woodland is believed to be of ancient origin, though there are also areas of more recent and open secondary woodland. Bitchet Common has acidic soils supporting mixed woodland: sessile oak Quercus petraea and beech Fagus sylvatica predominate together with coppice of birch Betula sp. and some sweet chestnut Castanea sativa. Other tree and shrub species present include hazel Corylus avellana, holly Ilex aquifolium, yew Taxus baccata, whitebeam Sorbus aria and rowan S. aucaparia. The ground flora is dominated by bracken Pteridium aquilinum and bramble Rubus fruticosus agg. whilst other species such as heather Calluna vulgaris, bilberry Vaccinum myrtillus and heath bedstraw Galium saxatile are also frequent. The plateau of One Tree Hill supports a similar vegetation, though here there is also dense scrub principally of hawthorn Crataegus monogyna, blackthorn Prunus spinosa and elder Sambucus nigra. The top of Shingle Wood, and the upper slopes of Broadhoath, Wet Bank and Martins Woods are also on similar soils to Bitchet Common. More mature trees are present in these areas and bluebell Hyacinthoides non-scripta is locally dominant in the ground flora. The valley of Martins Wood contains damp, more base-rich soils. Coppiced ash Fraxinus excelsior often predominates here though there is also much hazel, field maple Acer campestre and alder Alnus glutinosa. Some large pedunculate oak Quercus robur standards occur. Bramble and bluebell are dominant in the ground flora of the drier areas whilst in the wettest parts they are replaced by species such as opposite-leave golden-saxifrage Chrysosplenium oppositifolium, pendulous sedge Carex pendula and great horsetail Equisetum telmateia. The ragstone escarpment supports woodland of varied composition. There is much neglected coppice of ash and hazel together with some mature beech. Mature wych elm Ulmus glabra was formerly quite frequent but many specimens have been killed by Dutch Elm Disease A range of species characteristic of relatively base-rich soils is found amongst the ground flora: this includes dog’s mercury Mercurialis perennis, early-purple orchid Orchis mascula and green hellebore Helleborus viridis, the latter species being scarce in Kent. Bryophytes (mosses and liverworts) are frequent, including a liverwort with a predominantly western distribution, Porella arboris-vitae -- found here at its only known locality in Kent. The escarpment is extremely steep in places and minor landslip are not infrequent. Such events open up the woodland and thus there are some areas containing dense scrub or ruderal vegetation. Although the invertebrate fauna has not been extensively, investigated, the ragstone escarpment in particular is known to support a variety of species of interest. The large and distinctive slug Tandonia rustica was discovered here, for the first time in Britain, in 1986. Also present are two nationally scarce* snails, the point snail Acicula fusca and Rolph’s door snail Macrogastra rolphii, both of which are typically found in ancient woodland. This is also the only known Kent site for the bristletail Dilta hibernica.
This large ancient woodland site near Ham Street is an important invertebrate locality of national significance. Several hundred invertebrate (mainly insect) species have been found there, including 39 nationally rare species (listed in the British Red Data Books: 2 Insects) and 134 nationally scarce species. Several species are known in Britain only from this locality. Traditional woodland management on this site has given rise to broadleaved woodland crossed by wide herb-rich grassy rides, with a number of marshy areas and pools. This traditional pattern has been severely altered in the last 40 years by modern forestry techniques; large areas have been clear-felled and replanted, resulting in dense conifer woodland of limited conservation interest. However, the diverse native woodland has survived in many areas in strips along rides, which together with the rides themselves and tall scrubby vegetation in young plantations provide the wide variety of inter-connecting micro-habitats needed by the many different invertebrate species. In addition the storm of October 1987 felled large areas of mature conifers, leaving open areas available for the natural regeneration of native woodland. Broadleaved woodland within the site is mainly composed of oak Quercus robur and hornbeam Carpinus betulinus with other trees including sallows Salix caprea and S. cinerea, aspen Populus tremula, birches Betula pendula and B. pubescens, field maple Acer campestre and wild service tree Sorbus torminalis. The woodland floor supports bramble Rubus fruticosus, wood sorrel Oxalis acetosella, primrose Primula vulgaris, and yellow archangel Lamiastrum galeobdolon. A large number of the scarcest species of invertebrate feed specifically on the foliage of several of the broadleaved trees and shrubs, the most significant of which are aspen and oak. The animals associated with aspen are exceptional: the lesser belle moth Colobochyla salicalis (not found elsewhere in Britain) and a rare micro-moth Nephopteryx hostilis feed on the foliage. A scarce longhorn beetle Saperda populnea causes galls on aspen stems, which are also inhabited by a rare micro-moth Cydia corallana. A rare weevil Dorytomus affinis, which feeds in aspen catkins has only been recorded in one other place in Britain recently. The foliage of oak supports a rare micro-moth Microthrix similella, the rare orange upperwing moth Jodia crocego, the rare 'scarce merveille-du-jour' moth Moma alpium and the rare dark and light crimson underwing moths, Catocala promissa and Catocala sponsa as well as a rare sawfly Pamphilius sylvarum. Other trees and shrubs support a rare leaf beetle Crococephalus sexpunctatus and the rare triangle moth Heterogenea asella. Many invertebrate species are dependent upon a variety of dead-wood habitats, and at Orlestone rare species include a jewel beetle Agrilus viridis, the beetles Tropideres sepicola, Tropideres niveirostris, Platypus cylindricus, Tomoxia bucephala and Cis coluber and a flat-bug Aradus aterrimus. Ponds and wet areas in the clay soils of the woodland support a further important range of species. The water beetle Limnebius crinifer has not been found elsewhere in Britain, and other rare species include the great silver water beetle Hydrophilus piceus, the water beetle Hydrovatus clypealis and a cranefly Molophilus lackschewitzianus. Scarce species include a northern heathland water beetle Acilus canaliculatus and 17 others. The rides and open areas within the woodland provide sheltered feeding areas for animals living in the surrounding woodland, and also support many species directly. The vegetation is acidic grassland, dominated by common bent Agrostis capillaris and creeping soft-grass Holcus mollis, with many broadleaved herbs including lousewort Pedicularis sylvatica, ling heather Calluna vulgaris and devil’s-bit scabious Succisa pratensis. Invertebrates dependent on these habitats include an exceptional number associated with goldenrod Solidago virgaurea including the rare micro-moth Platyptilia calodactyla. Other invertebrates of these open areas include the toadflax brocade moth Calophasia bunula and a solitary wasp Symmorphus connexus; many scarce species include pear-bordered fritillary butterfly Boloria euphrosyne living at the edge of rides. The wide variety of habitats within the site also supports a diverse bird community: breeding species include lesser-spotted woodpecker Dendrocopos minor, nightingale Lucinia segarhynchos, hawfinch Coccothraustes coccothraustes, crossbill Loxia curvirostraand woodcock Scolopax rusticola.
This site includes areas of species-rich chalk grassland, and chalk scrub, and woodlands on a variety of soils. It supports a range of scarce and rare invertebrates. The site lies in the valley where the River Darent has cut through the chalk escarpment. Both chalk and overlying deposits are close to the surface and these different rock types produce varied soils, which on the hill tops are clayey and poorly drained while others, mostly on the steep slopes, are thin, calcareous (chalky) and freely draining. Much of the chalk downland was traditionally managed by grazing, mainly by sheep, which over centuries led to the development of very species-rich chalk grassland. A lack of grazing in recent decades has led to an overgrown form of this grassland over much of the site which is dominated by upright brome grass Bromus erectus. This is still very diverse, supporting over a hundred plant species. Other plants in the sward include sheep’s fescue grass Festuca ovina, red fescue Festuca rubra, bird’s-foot trefoil Lotus corniculatus, salad burnet Sanguisorba minor, rough hawkbit Leontodon hispidus, ribwort plantain Plantago lanceolata, fragrant orchid Gymnadenia conopsea, stemless thistle Cirsium acaule, quaking grass Briza media and devil’s bit scabious Succisa pratensis. Two nationally scarce1 plants are found growing here: man orchid Acerus anthropophorum and chalk milkwort Polygala calcarea. The formerly widespread scrub species juniper Juniperus communis occurs here at one of its last Kent localities. Much of the grassland areas grade into woodland through an intermediate scrub phase. Typically it is dominated by hawthorn Crataegus monogyna, ash Fraxinus excelsior, roses Rosa species, with traveller’s-joy Clematis vitalba, privet Ligustrum vulgare, black bryony Tamus communis and a variety of calcicolous (chalk-loving) species. The scrub communities vary greatly in age from a few years to a number of decades. The woodlands vary according to the underlying geology and contain both ancient2 and more recent sites. Areas on the deposits overlying the chalk are dominated by ash, pedunculate oak Quercus robur standards, downy birch Betula pubescens, field maple Acer campestre, hazel Corylus avellana, and sweet chestnut Castanea sativa. The ground flora is dominated by bramble Rubus fruticosus but includes a variety of other woodland species such as bluebell Hyancinthoides non-scripta, yellow archangel Lamiastrum galeobdolon and giant fescue grass Festuca gigantea. The scarp slope woods are mainly beech Fagus sylvatica woodlands which grade into ash-field maple woodlands at the foot of the scarp. The stands contain a range of tree species including yew Taxus baccata, ash, field maple, whitebeam Sorbus acuparia, silver birch Betula pendula, hornbeam Carpinus betulus, wych elm and sycamore Acer pseudoplatanus. The open canopy produced by the storm of October 1987 has encouraged a ground flora dominated by bramble with traveller’s-joy, ivy Hedera helix, wood false-brome grass Brachypodium sylvaticum and other woodland species. The variety of habitats support outstanding communities of woodland and chalk grassland invertebrate species. Amongst the nationally scarce*1 species present are moths: plumed prominant Ptilophora plumigera which feeds on field maple and Eudonia delunella which feeds on lichens and mosses on the trunks of ash, apple Malus species and occasionally on elms Ulmus species. A scarce hoverfly Cheilosia soror is present, found on the chalk downs visiting umbels in glades of woods. It has been reported to breed in truffles.
This site is a good representative of long established woodland on chalk soils in Kent. It is largely hazel and hornbeam coppice under oak standards, with diverse rub and ground layers. Several plant species characteristic of calcareous soils are present, including the uncommon lady orchid Orchis purpurea. The wood also contains an outstanding assemblage of invertebrates which includes the rare wasp Crossocerus distinguendus and there is also a large breeding bird community. The wood lies on a south-east facing slope, and a dry valley runs up through the centre of the site. A strip of chalk grassland runs along the south-western boundary; on the other boundaries and within the wood are earth banks marked by pollards of oak and ash, indicating the ancient origin of the wood. Much of the woodland is hazel and hornbeam coppice under standards of pedunculate oak, but sweet chestnut coppice is also abundant, especially in the north-western part of the wood. Other coppiced species include field maple, ash and birch, whilst mature tree species include ash, whitebeam, beech, birch and yew. There are dense stands of yew adjacent to the strip of chalk grassland and towards the north eastern part of the wood where there has been some recent coppicing. There are also some mature conifers scattered throughout the wood but mainly located towards the southern corner; these probably date from the turn of the century. The shrub layer includes hawthorn and several species characteristic of chalk soils, such as buckthorn Rhamnus catharticus, wild privet Ligustrum vulgare, wayfaring tree Viburnum lantana and guelder rose V. opulus. Bramble, dog’s mercury Mercurialis perennis and bluebell Hyacinthoides non-scripta are the principal components of the ground flora, which also contains the less common species wild liquorice Astragalus glycyphyllos and columbine Aquilegia vulgaris. Several uncommon species indicative of long established woodland occur, including wood spurge Euphorbia amygdaloides, een hellebore Helleborus viridus, stinking iris Iris foetidissima and herb paris Paris quadrifolia, and the orchids: lady orchid Orchis purpurea and butterfly orchid Platanthera chlorantha. Ferns are frequent and include buckler fern Dryopteris dilatata, narrow buckler fern D. carthusiana and male fern D. filix-mas. The strip of calcareous grassland along the south-western boundary is dominated by the grasses tor grass Brachypodium pinnatum and sheep’s fescue Festuca ovina, but the herb-rich sward also contains nettle-leaved bellflower Campanula trachelium and the characteristic downland species dwarf thistle Cirsium acaule, common rockrose Helianthemum nummularium and horseshoe vetch Hippocrepis comosa. Many of the woodland shrub species are also present, together with spindle Euonymus europaeus, dogwood Cornus sanguinea, and elder Sambucus nigra. Broom Cytisus scoparius and trailing St John’s wort Hypericum humifusum are present on less calcareous soils, and in the lower part of the dry valley are several clearings dominated by bracken and bramble. Invertebrates recorded in the wood include two rarities; the wasp Crossocerus distinguendus and the fly Stratiomys potamida, and several uncommon species including the woodland grasshopper Omocestus rufipes, plumed prominent moth Ptilophora plumigera, satin lutestring moth Tetheella fluctuosa and a butterfly, the Duke of Burgundy fritillary Hamearis lucina. Amongst the breeding bird species present are nightingale, nuthatch, green and great spotted woodpeckers and tawny owl.
The interest of this site is centred on the unimproved grassland on the west-facing slope of a dry valley. Dense scrub is present on the upper slope. The grassland is especially noted for its orchids including the nationally rare late spider orchid Ophrys fuciflora which is restricted to a few sites in East Kent. A number of other scarce plants also occur. The grassland, grazed by sheep and cattle, is dominated by tor-grass Brachypodium pinnatum and fescues Festuca species. A wide range of typical chalk downland plants are also present including dwarf thistle Cirsium acaule, lady’s bedstraw Galium verum, bird’s-foot trefoil Lotus corniculatus, common milkwort Polygala vulgaris and salad burnet Poterium sanguisorba. Columbine Aquilegia vulgaris also occurs here and the scarce slender bedstraw Galium pumilum is found at the north end of the site. The site is well known for its orchids with at least ten species having been recorded. Fragrant orchid Gymnadenia conopsea and common spotted-orchid Dactylorhiza fuchsii are probably the most numerous. Uncommon species include lady orchid Orchis purpurea and musk orchid Herminium monorchis, both of which flower intermittently. The latter is only found in a few sites in SE Kent and here can sometimes number several hundred flowering spikes. Another interesting feature of the site is the colony of the rare monkey orchid Orchis simia which was introduced here by seed in 1958. It was first seen in flower in 1965 and since then the number of flowering spikes has increased to over 20 by 1983. Hawthorn and blackthorn scrub, with some neglected hazel coppice is present on the deeper soils at the top of the slope. This is very dense in places with little ground vegetation present. Elsewhere the scrub is more open with some tall growth of bracken and brambles. The bracken and also thistles are encroaching on the grassland at the bottom of the slope. Typical scrubland birds breed in this area including nightingales.
The site includes areas of chalk grassland, scrub and woodland. The grassland is of the upright brome Bromus erectus, sheep’s fescue Festuca ovina type and is extremely herb rich, with one nationally rare plant species occurring. Among the many chalk downland herbs to be found here are salad burnet Poterium sanguisorba, rockrose Helianthemum chamaecistus, horseshoe vetch Hippocrepis comosa and autumn gentian Gentianella amarella. In addition to the nationally rare Kentish milkwort Polygala austriaca other uncommon species of plants are also found including several orchids for example man orchid Aceras anthropophorum, fragrant orchid Gymnadenia conopsea, and pyramidal orchid Anacamptis pyramidalis. The upper part of the woodland, on the clay with flints soil, is predominantly hornbeam coppice, although Stone Acre Wood is more varied, with oak, ash and wild cherry among others. The woodland floor is covered by bluebells Hyacinthoides non-scripta, dog’s mercury Mercurialis perennis, brambles Rubus fruticosus and some wood sorrel Oxalis acetosella and yellow archangel Galeobdolon luteum. The steeper slopes are mainly hazel coppice with large beech trees, and the ground flora here is more varied, including several scarce plants, such as stinking iris Iris foetidissima, fly orchid Ophrys insectifera, and lady orchid Orchis purpurea, the last is another species restricted to Kent. There are also small areas of scrub on the woodland edge, of hawthorn and various chalk-loving species such as wayfaring tree.
The River Beult flows for most of its length over Wealden clay which influences its ecology. It is one of the few clay rivers in England which retains a characteristic flora and fauna. This type of river occurs predominantly in central England and has usually been canalised for land drainage purposes. The Beult flows through an agricultural catchment with sheep and cattle pasture, orchards and arable land. River flows are dependent on surface run-off and weirs are placed in spring to maintain levels. In common with many lowland rivers, the Beult has suffered some enrichment with phosphate and nitrate from sewage effluent and agricultural run-off. The section of river being notified, from Smarden to the Medway confluence, excludes the upper river which is ditch-like with an impoverished fauna and flora.
The adjacent agricultural land use significantly affects these riverside plant communities, which in turn influence the insect and bird life. The most diverse plant communities occur where the river bank is relatively shallow and grades into a shallow berm grazed by cattle. The cattle-poached water edge supports fool’s water cress Apium nodiflorum, brook lime Veronica beccabunga, blue water-speedwell Veronica anagallis- aquatica, water figwort Scrophularia auriculata and water mint Mentha aquatica. Where the river bank is inaccessible to grazing animals, bulrush and branched bur-reed Sparganium erectum, reed canary grass Phalaris arundinacea, or reed sweet-grass Glyceria maxima become dominant. The river bank next to arable fields has weedy vegetation of nettle Urtica dioica and thistles Cirsium spp, due to fertiliser run-off and pesticide spray drift.
This site contains the most important sand dune system and sandy coastal grassland in South East England and also includes a wide range of other habitats such as mudflats, saltmarsh, chalk cliffs, freshwater grazing marsh, scrub and woodland. Associated with the various constituent habitats of the site are outstanding assemblages of both terrestrial and marine plants with over 30 nationally rare and nationally scarce species, having been recorded. Invertebrates are also of interest with recent records including 19 nationally rare3, and 149 nationally scarce4 species. These areas provide an important landfall for migrating birds and also support large wintering populations of waders, some of which regularly reach levels of national importance5. The cliffs at Pegwell Bay are also of geological interest.
The ornithological interest of Sandwich Bay and Hacklinge Marshes is centred on the large numbers of waders and wildfowl which use the area in winter and during the Spring and Autumn migrations. Dunlin Calidris alpina is usually the most common wader present, found particularly on the mudflats where the rich invertebrate fauna also attracts a wide range of other common species such as oystercatcher Haematopus ostralegus, curlew Numenius arquata, and redshank Tringa totanus. Grey plover Plurialis squatarola and sanderling Calidris alba both overwinter in nationally important numbers5, whilst ringed plover Charadrius hiaticula also occurs in nationally important numbers5 during migration. Wildfowl that occur on the site include mallard Anas platyrhynchos, shelduck Tadorna tadorna and occasionally brent goose Branta bernicla. Many of the birds use more than one habitat, some for example feed on the mudflats at low tide and then move up to roost on the saltmarsh or grazing marsh. Breeding birds include ringed plover, oystercatcher and little tern Sterna albifrons, a species specially protected by law and listed on Schedule 1 of the Wildlife and Countryside Act 1981. Inland areas are also of interest supporting two nationally rare species of breeding birds.
This classic coastal section is one of the best known Palaeogene sites in Britain having been the focus of scientific study since the eighteenth century. The cliff and foreshore section between Warden and Minster comprise Eocene London Clay, capped by Pleistocene sediments except between East End and Cliff Farm where the cliff intersects an outlier of the Eocene Virginia Water Formation. This is the only extant section of the upper part of the London Clay and is geographically the most extensive section of this Formation in Britain. Some of the most detailed studies of Palaeogene stratigraphy have been produced for this section. Five informal divisions (A–E) have been recognised for the London Clay of which divisions C, D & E are exposed. The stratigraphical and palaeoenvironmental significance of the site is a reflection of its extremely well preserved fossil fauna and flora. A considerable invertebrate fauna has been recovered including bivalves, gastropods, brachiopods and nautiloids. Also encountered are the articulated remains of crabs and lobsters and occasionally well preserved insect remains. There is a particularly abundant microfossil fauna which has been used as a basis for defining the stratigraphical divisions A–E of the London Clay. Fossil vertebrates are equally important and here include fish, reptiles and birds. Some of the most important fossil vertebrate remains occur in resistant nodules within the London Clay. Bony material is also often concentrated on the beach from otherwise fairly unproductive horizons. Agassiz’s classic work of the 1840’s figures many fish from the Sheppey section. The fossil fish uniquely include articulated cartilaginous shark remains and complete fish skulls. More than 160 fish species (including sharks, rays and bony fish) are recorded from this site for many of which this is the type locality. Since the 1820’s the site has beenwell known for its fossil reptiles. These include turtles Argillochelys, Chrysemys, Eospargis, Puppigerus, Trionyx for which this is the most prolific Tertiary site in Britain, crocodiles Crocodylus, and snakes Palaeophis. The site is also a key avian palaeontological site having yielded the first named fossil bird species, Halcyornis toliapicus (related to the kingfisher), in 1825. Since then 16 families (representing 12 Orders) have been identified and for some 20 species this is the type locality. The site shows the presence of a diverse fauna of shore and sea birds, as well as a large range of land birds from open and forest habitat. This site is the richest palaeobotany site in the London Clay. Divisions D and E have yielded the most extensive Eocene fruit and seed flora, with over 300 species being recorded. The flora is dominated by tropical lianas and also the coconut Nipa. This is the type locality for 285 species and 66 genera of plant. 200 of these species and 23 genera are unique to the Tertiary sediments of this site. Present day active processes have also been studied in considerable detail. At Warden Point, and to its west, a series of impressive, deep-seated, rotational landslips (bench shaped in plan) occur in the London Clay. Characteristically, each slip extends along the coast for distances between four and eight times the cliff height. The back-tilted blocks produced by failure are broken down by shallow slides and mudflows, the debris being removed by marine erosion. This in turn results in a progressive steepening of the cliff, and thus in further landslipping. This is the best locality in Britain to observe the cycle of rotational landslip typical of soft coasts.
The South Thames Estuary and Marshes SSSI from Gravesend to the eastern end of the Isle of Grain forms a major component of the Greater Thames Estuary. The site consists of an extensive mosaic of grazing marsh, saltmarsh, mudflats and shingle characteristic of the estuarine habitats of the north Kent marshes. Freshwater pools and some areas of woodland provide additional variety and complement the estuarine habitats. The site supports outstanding numbers of waterfowl with total counts regularly exceeding 20,000. Many species regularly occur in nationally important1 numbers and some species regularly use the site in internationally important2 numbers. The breeding bird community is also of particular interest. The diverse habitats within the site support a number of nationally rare3 and scarce4 invertebrate species and an assemblage of nationally scarce plants.
The mudflats attract large numbers of feeding waders and wildfowl with the site being regularly used by redshank Tringa totanus in internationally important numbers. There is evidence from recent winter low-water counts that knot Calidris canuta and dunlin Calidris alpina exceed internationally importantnumbers when feeding on the mudflats. These counts also indicate that avocet Recurvirostra avosetta and ringed plover Charadrius hiaticula regularly exceed nationally important numbers. During the high tide period, waterfowl disperse to roosts in marshes in north Kent and Essex. Nevertheless, high tide counts for this site clearly reveal species regularly reaching nationally important numbers in winter including European white-fronted goose Anser albifrons spp albifrons, shelduck Tadorna tadorna, gadwall Anas strepera, teal Anas crecca, pintail Anas acuta, shoveler Anas clypeata, grey plover Pluvialis squatarola, curlew Numenius arquata and black- tailed godwit Limosa limosa. In addition, nationally important numbers of grey plover, curlew, black-tailed godwit, redshank and greenshank Tringa nebularia occur during autumn passage with redshank maintaining their nationally important numbers on spring passage. During the breeding season the south Thames marshes support an outstanding assemblage of breeding birds including rare5 species such as garganey Anas querquedula, pintail, avocet and bearded tit Panurus biarmicus. Specially protected birds6 found within the site include hen harrier Circus cyaneus, short-eared owl Asio flammeus, ruff Philomachus pugnax, common tern Sterna hirundo, avocet and golden plover Pluvialis apricaria.
The saltmarshes support characteristic vegetation dominated by the saltmarsh grasses Puccinellia, the glassworts Salicornia, sea aster Aster tripolium, sea lavender Limonium vulgare and sea purslane Halimione portulacoides, with nationally scarce plants such as golden samphire Inula crithmoides4 and Puccinellia fasciculata4. The grazing marsh complexes, including seawalls, counterwalls, fleets, dykes, runnels and seasonally wet depressions provide suitable conditions for a wide range of plants and animals. The grassland habitats range from the damp muddy areas near the dykes, where characteristic plants include divided sedge Carex divisa4, small goosefoot Chenopodium botryodes4 and golden dock Rumex maritimus4, to the dry seawalls and counterwalls which support scarce species in addition to many widespread plants. These scarce plants include slender hare’s ear Bupleurum tenuissimum4, sea clover Trifolium squamosum4 and sea barley Hordeum marinum4, all of which are more abundant in the Thames estuary than elsewhere in Britain. Some seasonally damp depressions in the grassland contain the bulbous foxtail grass Alopecurus bulbosus4 whilst the more level turf is dominated by a variety of grasses including other foxtails Alopecurus, bents Agrostis, rye-grass Lolium perenne and fescues Festuca, with various herbs such as clovers Trifolium and buttercups Ranunculus also present. The rare and specially protected least lettuce Lactuca saligna7 which was previously recorded on seawalls in this site may still survive. The dykes and fleets which are an integral part of the grazing marsh have a range of salinities and consequently support an interesting range of plants. Those nearest the sea tend to be the most brackish, and generally have sea club-rush Scirpus maritimus, common reed Phragmites australis and fennel pondweed Potamogeton pectinatus as the most abundant species; some also include nationally scarce species such as brackish water-crowfoot Ranunculus baudotii4. In the freshwater dykes further inland there is a greater variety of species, plants such as branched bur-reed Sparganium erectum and reed-maces Typha spp. may become dominant. Nationally scarce plants associated with the dykes include soft hornwort Ceratophyllum submersum4 with water soldier Stratiotes aloides4 present in dykes near Higham. The mudflats have beds of eelgrass including Zostera angustifolia4 and Z. noltii4 and the Allhallows region of the site has areas of vegetated shingle with the nationally scarce sea kale Crambe maritima4 present.
This site supports a diverse invertebrate fauna and includes nationally rare3 beetles, flies and true bugs. The ‘scarce emerald damselfly’ Lestes dryas, listed in the British Red Data Book*, in the Cliffe area of the site. In addition, 100 nationally scarce species of invertebrate have been recorded including Lejops vittata (a hoverfly), Saldula opacula (a shorebug) and the dotted fan-foot moth Macrochilo cribrumalis, all of which are restricted to wetland, estuarine or grazing marsh habitats. The water beetle fauna is of particular interest and includes four species of Bagous (aquatic weevils), three species of Berosus and the great silver water beetle Hydrophilus piceus.
This wetland site located in the Stour valley contains a wide range of habitats including open water, extensive reedbeds, scrub and alder carr which together support a rich flora and fauna. The vegetation is a good example of a southern eutrophic flood plain and a number of rare plants are found here. The invertebrate fauna is varied and several scarce moths have been recorded in recent years. The site is also of ornithological interest with its diverse breeding bird community. Two rare British birds cetti’s warbler and bearded tit, regularly breed in nationally significant numbers.
In the western part of the site are a number of disused and flooded gravel pits with many spits and islands. In places there is a fringe of aquatic vegetation although some areas have been eroded by boating and angling. Willow and bramble scrub is well developed around the margins and also on the relatively undisturbed islands. A variety of birds use the lakes for breeding and wintering. Notable among the breeding birds are great crested grebe and tufted duck: also the rare cetti’s warbler which favours the low bramble scrub.
A number of scarce fen plants occur in areas where the reed has been cut, and also along the open dykes intersecting the reedbeds. Species include greater bladderwortUrticularis vulgaris, greater spearwort Ranunculus lingua and bog bean Menyanthes trifoliata. These dykes also contain some rare aquatic plants, for example sharp-leaved pondweed Potamogeton acutifolius and rootless duckweed Wolffia arrhiza.
The large area of grassland to the east of the reedbeds is mainly cattle-grazed pasture with intersecting dykes. The flora is similar to that described above, although in some places the dykes are choked with reed. Waders such as redshank, lapwing and snipe breed on the fields. In winter and at times of passage flocks of waders, ducks and sometimes geese feed and roost here.
This site, extending almost uninterrupted from Swalecliffe to Ramsgate, comprises mainly unstable cliff and foreshore (including shingle, sand and mudflats), with smaller areas of saltmarsh, coastal lagoons, coastal gill woodland and cliff-top grassland. There are a number of biological, geological and geomorphological features of interest within the site.
Within this site strips of grassland along the seawalls are dominated by couches Elymus species and fescues Festuca species. Other flowering plants include the nationally rare** hog’s fennel, found along the seawall at Plumpudding Island, and some nationally scarce* species such as slender hare’s ear Bupleurum tenuissimum and sea clover Trifolium squamosum. Some of the more common species recorded include spiny restharrow Ononis spinosa and grass vetchling Lathyrus nissolia. The drift line debris in the vicinity of Swalecliffe supports the only population of the nationally rare** isopod (woodlouse) Eluma purpurescens on mainland Britain, and the cliffs around Bishopstone support two nationally rare** digger wasps Ectemnius ruficornis and Alysson lunicornis. It is likely that further survey may reveal additional rare or scarce invertebrate species in the site. These particular cliffs also support one of the two largest sand martin Riparia riparia colonies in Kent.
This 10 km stretch of the chalk escarpment to the north of Maidstone includes representative examples of woodland, scrub and unimproved grassland habitats on chalk, which support a number of rare** and scarce* species of plants and invertebrates. The Culand Pits are also of importance because of their rich and unique fossil fauna which includes a variety of fish and reptiles.
Although most of the woodland is recent in origin, it has already acquired a rich community of plants and animals. The tree canopy is dominated by various proportions of beech Fagus sylvatica, ash Fraxinus excelsior, whitebeam Sorbus aria, wild cherry Prunus avium, silver birch Betula pendula and yew Taxus baccata. Understorey shrubs include hazel Corylus avellana, hawthorn Crataegus monogyna, midland hawthorn C. laevigata, elder Sambucus nigra and privet Ligustrum vulgare, while the ground flora includes dog’s mercury Mercurialis perennis, ivy Hedera helix, lords-and-ladies Arum maculatum and spurge laurel Daphne laureola. Scarce* plants include lady orchid Orchis purpurea and stinking hellebore Helleborus foetidus. Box Buxus sempervirens, a rare** small tree, is native here at one of a handful of sites in the south-east. The storm of October 1987 has added variety to the woodland by opening up some of the areas with a closed canopy. Scrub on the site includes the full range of succession from open grassland to the woodland already mentioned. Scattered clumps of hawthorn and wild rose Rosa spp. (including the scarce Kent+ species R. rubiginosa) gradually merge and a varied scrub develops, with more than a dozen shrub species, including dogwood Cornus sanguinea, privet, hazel, hawthorn, wayfaring tree Viburnum lantana, yew and the rare** box. Eventually tree species become dominant and woodland develops. The ground flora, which begins as rank chalk grassland, becomes shaded by the developing scrub, eventually resembling that of the woodland. Chalk grassland survives as fragments within the scrub, and a number of larger areas also occur. The most open areas are dominated by fine grasses including red and sheep’s fescues Festuca rubra and F. ovina, with low-growing broadleaved plants such as stemless thistle Cirsium acaule, fairy flax Linum catharticum, bulbous buttercup Ranunculus bulbosus, wild thyme Thymus praecox and salad burnet Sanguisorba minor. Most of the grassland is taller, dominated by upright brome Bromus erectus with broadleaved plants including hairy violet Viola hirta, marjorum Origanum vulgare and cowslip Primula veris. Other plants in the grassland include: a number of orchids – fragrant orchid Gymnadenia conopsea, common spotted orchid Dactylorhiza fuchsii, twayblade Listera ovata and pyramidal orchid Anacamptis pyramidalis; several plants scarce in Kent+ such as chalk milkwort Polygala calcarea, dropwort Filipendula vulgaris, burnet rose Rosa pimpinellifolia and adder’s-tongue fern Ophioglossum vulgatum; several nationally scarce* species such as man orchid Aceras anthropophorum and ground pine Ajuga chamaepitys; and the nationally rare** meadow clary Salvia pratensis. The site supports a rich insect assemblage typical of southern calcareous grassland, including a number of uncommon species. The moths (Lepidoptera) of Culand Pits have been best studied and the fauna includes 11 scarce* species, most notable of which is the straw belle Asptitates gilvaria, and one rare** species. Oncocera obductella all associated with chalk grassland plants. A further 6 scarce* species of grasshopper (Orthoptera), bug (Heteroptera) and beetle (Coleoptera) have been recorded, as well as a rare bug Hallodapus montandoni, which is associated with ants in short grassland: these species are all typical of chalk grassland. In addition 3 scarce* woodland moths and one scarce* beetle Mordellistena neuwaldeggiana typical of woodland edge, are known from the site.
The mosaic of habitats within the site and in particular the species-rich grassland, support an outstanding invertebrate community with records of at least 86 nationally rare or scarce species. The site is important for moths and butterflies and 24 of those recorded recently are nationally scarce including the plumed prominent moth Ptilophora plumigera and the Duke of Burgundy butterfly Hamearis lucina. The rare black-veined moth Siona lineata occurs here at one of its very few locations in Britain and is specially protected under Schedule 5 of the Wildlife and Countryside Act 1981.
Below are links to map pages of each area of Special Scientific interest in Kent
Below are links to map pages of each area of Special Scientific interest in Kent. Here you will be able to view various maps of each location including Aerial, Satellite, Dual View and even old Ordnance Survey maps with a modern day Google map overlay, Cycle routes and much more.