Botanical Journal of the Linnean Sociery (1989), 101: 103-109. Lichens at Dungeness JACK R. LAUNDON Department SW75BD of Botany, British Museum (Natural History), Cromwell Road, London LAUNDON,J. R., 1989. Lichens at Dungeness. The lichen vegetation at Dungeness is reviewed. The most important lichen communities are of three types. Firstly, there are the crustose lichens which colonize the bare pebbles. Secondly, the tracts of rich Cladonia turf which form the lichen heath and which play a major role in the vegetation cycle. Thirdly, there are the epiphytes on Prunus scrub. In addition, lichens on artificial substrates, especially wooden fences, are noteworthy. About 150 species occur, amongst the most interesting being Cladonia mitis, Lecanora helicopis, Lecidea insidiosa, Parmelia soredians, Rinodina aspersa and Usnea glabrata. A new combination is made in the genus Porpidia. The term 'bird farming' is published. The fragmentation of the vegetation by building and gravel extraction receives critical comment. ADDITIONAL KEY WORDS:-Bird farming- conservation. CONTENTS 103 104 105 106 108 109 Introduction . Crustose lichens on pebbles Lichen heath . Scrub. Artificial substrata. References INTRODUCTION Shingle beaches are amongst the least hospitable habitats for plants and animals. The ground is composed of rounded pebbles, over which there is initially little or no soil. The pebbles are unstable, in as much as they are subject to movement by wave action immediately by the coast and trampling by feet or vehicles elsewhere. There is no shade from the heat of the sun and little respite from the wind carrying salt spray. In such extremes only specially adapted plants and animals can flourish, and amongst these are certain lichens. These are poor competitors and need open vegetation for survival. Each lichen consists of a fungus and a photobiont (an alga or cyanobacterium) living together, the latter providing the nutrients. This mode of nutrition enables lichens to exist in places which are inhospitable to other plants. There are about 1500 species in Britain. From Dungeness 148 lichen species are reported, plus another ten requiring confirmation of identification. Specimens of many of these are housed in the herbarium of the British Museum (Natural History), London; those studied for the writing of this paper are cited '(BM!)'. 103 0024-4074/89/090103+07 $03.00/0 © 1989 The Linnean Society of London 104 J. R. LAUNDON At Dungeness the shingle consists almost entirely of flint pebbles which the sea has, in the past, heaped up into ridges. Five separate beaches have been formed successively from west to east, with belts of marsh between them. The five are Jury’s Gap, Forelands, Holmstone, West Ripe, and Denge Beach. This last was mostly formed between about AD 750 and the present time (Lewis & Balchin, 1940: fig. I ) , and is the most extensive and important. It now extends inland for a distance of 5 km. The pebbles are acid and, therefore, calcicolous plants are scarce. Along the southern shore there is a prominent, largely natural ridge of unstable shingle. The only common plant here is seakale, Crambe maritima L., which grows on top of the ridge and down the landward side. This plant is confined to the littoralfringe or drift line, with no associated lichens, except for a few growing on driftwood. CRUSTOSE LICHENS ON PEBBLES Behind the southern coastal ridge the bare shingle is colonized by crustose lichens. These are pioneer species-the first colonizers, which become crowded out when growing on other rocks. They are small and often poorly developed. The dominant species on pebbles adjoining the drift line is Rhizocarpon richardii (Lamy ex Nyl.) Zahlbr. (R. constrictum Malme). This forms a zone 300 m wide, extending from Pen Bars westwards to the Wicks, a distance of 5 km where it blackens the pebbles, with up to 25% cover. An interesting lichen of this zone is Lecanora helicopis (Wahlenb. ex Ach.) Ach., which is frequent on sheltered pebbles at Abnor Pit, near Galloways, alongside a salt-marsh (BM!). This species is quite rare in lowland Britain. Rhizocarpon richardii declines away from the drift line but is replaced by other encrusting lichens, of which Buellia aethalea (Ach.) Th.Fr. is much the most abundant. Rhizocarpon obscuratum (Ach.) Massal. is also common, whilst Aspicilia caesiocinerea (Nyl. ex Malbr.) Arnold and the dark foliose lichen Parmelia glabratula (Lamy) Nyl. subsp. fuliginosa (Fr. ex Duby) Laundon are frequent on sheltered pebbles. The sorediate Rinodina aspersa (Borrer) Laundon (Buellia aspersa (Borrer) P. James, Rinodina fatiscens (Th.Fr.) Vainio) (BM!), described from flints in Sussex, is now scarce. Two other sorediate lichens occurring on pebbles are Porpidia soredizodes (Lamy ex Nyl.) Laundon, comb. nov.* and P. tuberculosa (Sm.) Hertel & Knoph, both of which are local. Another local species is Lecidea erratica Korber, distinguished by the presence of abundant pycnidia. This lichen has many noteworthy synonyms, including L. chalybeiza Nyl., L. expansa Nyl. ex Mudd (1861) non L. expansa Chevall. (1826), and L. myriocarpoides Nyl. Research on the taxonomy and nomenclature of Aspicilia caesiocinerea, Buellia ocellata (Flotow) Korber (B. verruculosa auct.) , Rhizocarpon richardii, and Rinodina aspersa has been carried out and published (Laundon, 1986a). The association Lecideetum erraticae was described from Dungeness (James, Hawksworth & Rose, 1977: 394-395). *Basionym: Lccidea crustulata [subsp.] soredizodes Lamy ex Nyl. in Flora, Jena 66: 534 ( 1 xii 1883). Type: France, Hautes-Pyrknkes, Cauterets, sapinikre du Riou, on slate, 22 vii 1883, “Ex Nyl.”, Lamy de la Chapelle, Lichens des environs de Cauterets . . . 1883 . . . fax. 11 p. 36 (PC!-holotype [TLC: stictic acid; medulla I-], HNyl. 16241 !-fragment, EM!-slide collection). LICHENS AT DUNGENESS 105 LICHEN HEATH Within the Rhizocarpon richardii zone, communities of Cladonia lichens begin to develop. The most common species near the sea is Cladonia rangiformis Hoffm. forming bushy clumps of whitish-grey forked thalli. Associated species are the yellow Cladonia foliacea (Huds.) Willd. and the grey Cladonia cervicornis (Ach.) Flotow, both characteristic of bare shingle with little surface humus. Ferry, Barlow & Waters (1989) have shown that the shingle is less acid at the coast than inland, which probably accounts for the different lichen flora near the sea. One of the main flowering plants in this community is Sedum anglicum Huds., the English stonecrop. Away from the sea, the development of the vegetation is related, at least to some extent, to the level of the water-table below the shingle surface. In hollows where water is present sallow (Salix spp.) scrub develops, and rich aquatic and marsh communities occur (Ferry & Henderson, 1984; Ferry & Waters, 1988). These are amongst the few natural freshwater pools on shingle in lowland Britain. Where the water-table comes within a metre of the surface, lichen heath and scrub develops. Where the shingle is very dry, the landscape is quite barren and only a few crustose lichens are found, as on the site of the current RSPB excavation at Walkers Outland. The absence of plant colonization on parts of Dungeness is especially interesting and controversial. Are these deserts really natural? Alongside the hollows, and on the ridges on the eastern side of Denge Beach, lichen heath has formed. In this community one of the reindeer lichens, Cladonia portentosa (Dufour) Coem., is dominant, associated with the moss Dicranum scoparium Hedw., the grass Festuca filiformis Pourret (F. tenuifolia Sibth.), sheep's sorrel (Rumex acetosella L.), and wood sage ( Teucrium scorodonia L.). This vegetation type is described by Ferry et al. ( 1989). Lichens establish only where a suitable anchorage is available and where humus has been formed from moss shoots and a variety of flowering plants, notably broom (Cytisus scoparius). A few other lichens occur in the lichen heath, but only Cladonia gracilis (L.) Willd. is constantly present, yet has low cover values. The most exciting lichen in this community is Cladonia mitis Sandst. Dungeness is the only locality in England for this otherwise arctic lichen. It is apparently a post-glacial relic, which survived the forest maximum in open coastal habitats near Dungeness; the Nottingham catchfly Silene nutans L. is believed to have survived in a similar way on nearby chalk cliffs (Rose, 1957: 68). In 1955 P. W. James and I collected Cladonia mitis between Lydd-on-Sea Station (now gone) and Dungeness Point (BM!); it was collected again from this area by P. W. James in 1958 (BM!), but has not been seen from there in recent years. Fortunately, it still grows on the Ministry of Defence Ranges (BM!), but there are only four plants present-perhaps the last four plants in England. Other members of the lichen heath include Cladonia ciliata Stirton var. tenuis (Florke) Ahti, Cladonia furcata (Huds.) Schrader, and Coelocaulon aculeatum (Schreber) Link. Between Pen Bars and Galloways, lichens which are normally corticolous (Evernia prunastri (L.) Ach., Hypogymnia physodes (L.) Nyl., Parmelia caperata (L.) Ach., and P. sulcata Taylor) are common on the shingle. However, the heath is remarkable for the extraordinary dominance of Cladonia portentosa and the low cover values of other lichens, and for its stability in occupying I06 J. R. LAUNDON the same areas over many decades, as shown by the study of old air photographs. Before 1958 Dungeness was undeveloped and unspoilt. I first visited it in 1952 and never expected that it would become so damaged in later years. In 1952 the landscape was idyllic. The best and most extensive area of lichen heath was to the west of the Grand Redoubt fortress. In 1958 everything changed. The Central Electricity Generating Board issued a Compulsory Purchase Order for land for a nuclear power station. The Nature Conservancy (1958) opposed the order at an enquiry, but they unfortunately lost the case. This decision in favour of the CEGB led the Nature Conservancy to make a grave error ofjudgment. In 1959 it abandoned plans for a proposed nature reserve because “repercussions of the power station on the remaining area shows conclusively that the future scientific interest will be too much reduced to qualify it for National Nature Reserve status” (Nature Conservancy, 1960: 38). Yet in 1977 it admitted that the “construction of a nuclear power station has detracted little from this value” (Ratcliffe, 1977: 52), no reduction in interest outside the power station having taken place. In the late 1950s large-scale gravel winning was established on the beaches (Findon, 1985: 16). The chief operator was the Amey Roadstone Corporation, a subsidiary of Consolidated Gold Fields Ltd. Their most controversial development was the digging of a large gravel-pit within the Royal Society for the Protection of Birds reserve next to the Open Pits. This is called Burrowes Pit, named in honour of Mr R. B. Burrowes, who devoted his savings to the conservation of the beach. It was begun in 1970 and completed in 1977. The RSPB obtained a substantial income from the sale of gravel royalties. In the year ended 31 March 1974 alone, it received E56304 in mineral royalties (Royal Society for the Protection of Birds, 1974: 7). It may be questioned whether this is taking bird farming” too far to engage in open-cast mining in what is regarded as a nature reserve. This and other gravel-pits have now fragmented the lichen heath and other shingle vegetation into a series of isolated pockets in contrast to its former continuous glory. The loss of the stone curlew, Burhinus oedicnemus (L.), as a breeding species from Dungeness (Scott, 1985:86) may reflect this fragmentation. SCRUB Scrub occurs on the shingle where conditions are suitable. In wet hollows it is of sallow (Salix cinerea L.). On drier shingle the scrub is of four types: gorse (Ulex europaeus L.), broom (Cytisus scoparius (L.) Link), blackthorn (Prunus spinosa L.), and holly (Ilex aquifolium L.). Old willow scrub has a good lichen flora; it is well described by Ferry & Waters (1984). It is especially noteworthy for the abundance of Lecanora confusa Almb., and for the occurrence of Parmelia reticulata Taylor, recorded from Salix between the Open Pits (Ferry & Waters, 1984: 154). Gorse forms a plagio-climax at Dungeness in disturbed areas. Its lichen flora has been little studied, but is considered to be of minor importance. Broom is *Bird farming is a term, introduced by Mr F. H. Brightman, to denote the artificial alteration of land to attract certain types of bird life. The Scrape at Minsmere RSPB Reserve in Suffolk is an outstanding example of the art. LICHENS AT DUNGENESS 107 much more interesting, because it is involved in a unique vegetation cycle on the lichen heath (Scott, 1965: fig. 6; Peterken & Hubbard, 1972: fig. 10). Broom colonizes shingle ridges inland from the coast. Plants die from the centre and their rotting wood forms a layer over the shingle. This rotting wood is colonized by cup lichens of the Cladonia chlorophaea (Florke ex Sommerf.) Sprengel complex. The wood decays away, Cladonia chlorophaea dies, and various flowering plants and lichens, especially Cladonia portentosa, replace it. Recolonization by Cytisus may occur again, and the cycle is then repeated. Several different chemotypes of the Cladonia chlorophaea complex occur on the dead broom, and have been studied by Ferry & Pickering (1989). Dungeness is one of the best places for work on this type of chemical variation in lichens. Transition zones from shingle to alluvial soils occur on the landward side of all the beaches. Both here and around the Open Pits colonization by prostrate blackthorn scrub is evident. The bushes are often richly covered with fruticose lichens, especially Evernia prunastri, Hypogymnia physodes and Usnea subjloridana Stirton. The nuclear power station has no overt effect on this lichen vegetation. The most interesting blackthorn lichen found in recent years (in 1976) is Usnea glabrata (Ach.) Vainio (BM!), long thought to be extinct in Britain. B. W. Ferry has found Usnea rubicunda Stirton recently on blackthorn on the west side of the Ranges. I remember seeing this red Usnea locally abundant on blackthorns at the Open Pits in 1955; it has, alas, long been extinct from Denge Beach. Fortunately, Usnea cornuta Korber ( U. injlata (Duby) Motyka) is still locally abundant on Walkers Outland. Other noteworthy lichens found on blackthorn include Bryoria fuscescens (Gyelnik) Brodo & D. Hawksw., collected by F. Rose and B.J. Coppins in 1968 (BM!), and Cetraria chlorophylla (Willd.) Vainio, seen in 1987. Before 1878, Nephroma laevigatum Ach. (Nephromium lusitanicum (Schaerer) Nyl.), Parmeliella plumbea (Lightf.) Vainio (Pannaria plumbea (Lightf.) Bory), Sticta fuliginosa (Hoffm.) Ach., Sticta limbata (Sm.) Ach. (BM!), and Teloschistesjlavicans (Swartz) Norman (BM!-last specimen collected by W. H. Hammond, received 1905) grew on the blackthorns "near the ponds" [i.e. Open Pits] (Holmes, 1878), but all are now extinct. Lobaria pulmonaria (L.) Hoffm. (BM!) and Lobaria scrobiculata (Scop.) DC. (BM!-on blackthorn) also occurred, the former covering "nearly an acre of ground profusely" "on the sand not far from the cultivated fields", the latter "Extremely abundant ... on the sandy ridges" (Holmes, 1878). The precise sites are unknown. These are all oceanic lichens which are very sensitive to air pollution; at Dungeness they were on the edge of their range. They became extinct probably early in the present century because of the rise in background air pollution which occurred in south Kent, as indicated by the spread of the pollution-tolerant lichen Lecanora conizaeoides Nyl. ex Crombie on to Denge Beach. Blackthorn is, of course, not the climax vegetation on the shingle. This is considered, by some, to be holly, which still forms open scrub on Holmstone Beach. About 300 ancient bushes, some well over 170 years old, remain, the relics of a wood which "probably originated naturally before the eighth century A.D." (Peterken & Hubbard, 1972: 571). The old word for holly is holm, and it seems probable that the beach [Holmstone] was named after the holly wood which covered it. A Saxon charter of c. 741 refers to a "wood called Ripp", ripae meaning shingle banks, now the name of the beach [West Ripe] next to Holmstone. In about 1539 Leland reported "Ther is a Place beyond Lydde, wher 108 J. R. LAUNDON as a great Numbre of Holme Trees groueth apon a Banke of baches throwen up by the Se, and there they bat Fowle, and kil many Birdes” (Leland, 1744: 133). Since this ancient woodland has never shown any signs of further development, it could be regarded as the climax. I t is unique in Britain. A younger holly wood (formed 1799-187 1) formerly occurred on Forelands Beach (Peterken & Hubbard, 1972: 568). Only very isolated bushes occur on the other beaches, all of which may have been planted. Peterken & Hubbard (1972: 568) consider that sheep grazing either eliminated or prevented the establishment of holly woodland on the eastern beaches in medieval times, where gorse scrub has long formed a plagio-climax in disturbed areas. Unfortunately, the lichen flora of the hollies on Holmstone Beach is not remarkable. Lecanora conizaeoides and the green alga Desmoccoccus olivaceus (Pers. ex Ach.) Laundon (Pleurococcus viridis (Agardh) Rabenh.) occur on live branches, these being replaced by Lecanora expallens Ach. and scattered macrolichens, such as Evernia prunastri, Parmelia sulcata Taylor, and Ramalina farinacea (L.) Ach., when the branches are old and dead, and the leaves have been lost. ARTIFICIAL SUBSTRATA Artificial substrata are prominent in parts of Dungeness. Lichens are absent from some, such as recent gravel pits and metal pylons, but are important on others, such as concrete buildings and posts, and wooden fences. Some artificial substrata are more important for lichens than for any other group of plants or animals, but unfortunately they have not been studied in detail. Several concrete bunkers are present as survivors from the Second World War or have been built for use on the ranges. Concrete posts are used as supports for wire fences. The concrete is often well-covered with common species of Caloplaca, Candelariella, Lecanora, Physcia sensu lato, and Xanthoria. The most interesting record is Caloplaca ruderum (Malbr.) Laundon, a species with a marked eastern distribution in Britain (Laundon, 1986b: fig. 26). Small plants were frequent on the concrete hemispherical hood of the ‘Listening Devices’ on eastern Denge Beach in 1983. An account of the Listening Devices is given by Ingrams in Godwin & Ingrams (1980: 151-152). Wooden posts, bordering the tracks of disused railway lines, often have an interesting lichen flora. Cyphelium inquinans (Sm.) Trevisan, Lecanora conizaeoides, and Lecanora varia (Hoffm.) Ach. are all common on erect railway sleepers, which form the posts of a fence on both sides of the disused railway on the south and east sides of Lydd Airport. However, the most interesting lichens have been found on fences further south. The most noteworthy of these is Lecidea insidiosa Th. Fr., a lichenicolous lichen collected by Dr T. D. V. Swinscow from a railing near Boulderwall on 4 March 1967 (BM!); this species grows on Lecanora varia, killing the fungal partner and taking over the alga to become lichenized. It is reported from only two other sites in the British Isles (Hawksworth, 1982: 385; the quoted date of collecting is erroneous). Dr Swinscow also collected the northern lichens Parmeliopsis aleurites (Ach.) Nyl. (BM!) and Pseudevernia furfuracea (L.) Zopf (BM!) from other railings on the same date. I n contrast, the southern lichen Parmelia soredians Nyl. was collected by P. W. James from a fence post near Hamilton Farm, also on 4 March 1967 (BM!). Both chemotypes (BM!) of LICHENS AT DUNGENESS 109 Pseudevernia furfuracea occur at Dungeness (Hawksworth & Chapman, 1971: figs2, 3). A few lichens occur on railway clinker. Stereocaulon vesuvianum Pers. was found by P. W. James on clinker by Lydd-on-Sea Station in 1958 (BM!). This railway line is now gone-like so much else at Dungeness. REFERENCES FERRY, B. W. & HENDERSON, A., 1984. The vegetation of natural freshwater pits at Dungeness-I: higher plants. Transactions of the Kent Field Club, 9: 143-153. FERRY, B. W. & PICKERING, M., 1989. Studies on the Cladonia chlorophaea complex at Dungeness, England. Lichenologist, 21: 67-77. FERRY, B. W. & WATERS, S. J. P., 1984. The vegetation of natural freshwater pits at Dungeness-II: lichens and bryophytes. Transactions of the Kent Field Club, 9: 153-158. FERRY, B. W. & WATERS, S. J. P., 1988. Natural wetlands on shingle at Dungeness, Kent, England. Biological Conservation, 43: 27-41. FERRY, B. W., BARLOW, S. & WATERS, S. J. P., 1989. The shingle ridge succession at Dungeness. Botanical Journal of the Linnean Socie!J, /01: 19-30. FINDON, R., 1985. Human pressures. In B. Ferry & S. Waters (Eds), Dungeness. Ecology and Conservation. Focus on .Nature Conservation, 12: 13-24. Peterborough: Nature Conservancy Council. GODWIN, F. & INGRAMS, R., 1980. Romney Marsh. London: Wildwood House. HAWKSWORTH, D. L., 1982. Notes on British lichenicolous fungi: IV . .Notes from the Royal Botanic Garden Edinburgh, 40: 375--397. HAWKSWORTH, D. L. & CHAPMAN, D. S., 1971. Pseudeverniafuifuracea (L.) Zopfand its chemical races in the British Isles. Lichenologist, 5: 51-58. HOLMES, E. M., 1878. The cryptogamic flora of Kent. Lichens. Journal of Botany, 16: 117-120, 209-212, 329345, 373-376. JAMES, P. W., HAWKSWORTH, D. L. & ROSE, F., 1977. Lichen communities in the British Isles: a preliminary conspectus. In M. R. D. Seaward (Ed.), Lichen Ecology: 295-413. London: Academic Press. LAUNDON,J. R., 1986a. Studies in the nomenclature ofBritish lichens II. Lichenologist, 18: 169-177. LAUNDON, J. R., 1986b. Lichens. Aylesbury: Shire. LELAND, J., 1744. The Itinerary of John Leland the Antiquary, 7. 2nd edn. Oxford: Fletcher & Pate. LEWIS, W. V. & BALCH IN, W. G. V., 1940. Past sea-levels at Dungeness. Geographical Journal, 96: 258-285. NATURE CONSERVANCY, 1958. Evidence of the .Nature Conservanry for the Public Inquiry into the Proposed .Nuclear Power Station at Dungeness, Kent, to he held at L_ydd, .New Romney, Kent, on 16 December 1958. London: Nature Conservancy. NATURE CONSERVANCY, 1960. Report of the .Nature Conservanry for the Year Ended 30th September 1960. London: Her Majesty's Stationery Office. PETERKEN, G. F. & HUBBARD,J. C. E., 1972. The shingle vegetation of southern England: the holly wood on Holmstone Beach, Dungeness. Journal of Ecology, 60: 547-572. RATCLIFFE, D. A. (Ed.), 1977. A .Nature Conservation Review, I. Cambridge: Cambridge University Press. ROSE, F., 1957. The importance of the study of disjunct distributions to progress in understanding the British flora. InJ. E. Lousley (Ed.), Progress in the Study of the British Flora: 61-78. London: Botanical Society of the British Isles. ROYAL SOCIETY FOR THE PROTECTION OF BIRDS, 1974. RSPB report & accounts 1973-74. Birds, 5 (5): 1-8 [separately paged in centre of the issue}. SCOTT, B., 1985. Dungeness: bird populations past and present. In B. Ferry & S. Waters (Eds), Focus on .Nature Conservation .No. 12, Dungeness Ecology and Conservation: 64-93. Peterborough: Nature Conservancy Council. SCOTT, G. A. M., 1965. The shingle succession at Dungeness. Journal of Ecology, 53: 21-31.
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