Field Bryology number 91

Reports of BBS meetings

Throughout the fo llowing section, new vice­ References county records are indicated with an asterisk (*). Nomenclature aims to fo llow Blackstock et al. Blackstock TH, Rothero GP, Hill MO. 2005. Census (2005). catalogue of British and Irish updated 2005. British Bryological Societyunpublishedreport. Download fr om http://www .britishbryologicalsociety.org.uk by fo llowing Resources>Downloads>Census Catalogue and clicking 'Interim Census Catalogue 2005'.

AGM and Bryological Symposium 2006, Hatfield

Agneta Burton

School of LifeSciences (D ivision of Geograp hy and Environmental Sciences), Un i­ versity of Hertfordshire, Ha tjieldAL l 0 9A B; m. a. [email protected]. uk

The Annual General Meeting and Bryological locally-based participants joined fo r the Sunday Symposium were held at the new DeHavilland field excursion. Abstracts of the papers, provided campus of the University of Hertfordshire on 8th- by the speakers, are presented below. 10th September 2006. The Symposium was at­ tended by 44 people and it was a pleasure to have After an extremely dry summer in the East of a number of new members, and others who had England provided a challenge of findinga suitable not attended an indoor meeting before, as well as site fo r a field excursion, which was ably met by members fr om across England, , Alan Outen whose account of the excursion can and two from mainland . Some additional be fo und at the end of this account.

Bryological Symposium The general theme included a number of papers on concerns and theories about species distributions. bryophytes and environmental change, with pres­ The Conversazione on Saturday evening pro­ entations on experimental and fieldapproaches to vided an opportunity to examine and comment examining responses to change and fo r conserva­ on poster displays of designs fo r the fo rthcoming tion purposes. In addition, presentations based BBS Field Guide as well as research posters, listed on field records fr om home and abroad, both in the penultimate part of this account. recent and from the past, were used to illustrate

34 Reports ofBBS meetings

Climate change and ultraviolet radiation: effects on stream bryophytes ja vier Ma rtinez-Abaigar and Encarnacion Nu iiez-0/ivera (Universidad de La Rioja, Logroiio, Sp ain)

Ultraviolet (UV) radiation is the part of the solar spectrum present levels of UV-B and of the presumably higher future extending from the X-rays to the visible/photosynthetic re­ levels of UV-B that could be reached as a consequence of gion. For biological purposes, the UV radiation is divided ozone depletion. We circumscribe this research to aquatic into three bands: the lethal UV-C (100-280 nm) , the mostly bryophytes fr om mountain streams. harmfulUV-B (280-315 nm) and the more innocuous UV-A (31 5-400 nm) . The stratospheric ozone layer absorbs com­ Our methodological approaches include laboratory and field pletely UV-C and thus protects the living organisms against studies. In the laboratory, UV-B is enhanced by adequate its destructive effects. However, the protection against UV-B lamps to simulate 20% ozone depletion, and the bryo­ is only partial, and thus a certain amount of UV-B reaches phyte responses have been assessed through morphological TheEarth's surface. UV-A is hardly influencedby the amount variables (colour and symptoms of cell degradation), and of ozone in the atmosphere. The amount of UV-B received physiological ones: the state of the photosynthetic appara­ depends not only on diverse natural factors (solar elevation, tus (concentration of chlorophyll and carotenoids, pigment altitude, clouds, aerosols and albedo), but also on the an­ indices showing vitality, photosynthesis rates, and chloro­ thropogenic depletion of the ozone layer caused· mainly by phyll fluorescence kinetics), respiration rates, DNA damage, emission of halocarbons. The ozone depletion is especially protein level, accumulation of UV-absorbing compounds, dramatic in the Antarctic continent, but significant ozone sderophylly index (the relationship between mass and area losses occur in the Arctic and mid-latitudes as well (5-12% of shoots), and growth. We have studied mainly since 1980). It is estimated that a 1 o/o ozone loss causes a two species: the Fontinalis antipyretica and the liverwort 1-2% increase in UV-B. An excessive UV-B exposure may jungermannia exsertifolia subsp. cordifolia. The most remark­ cause damage to living organisms. In humans, the most com­ able results obtained by our group will be briefly explained. mon health risks affect skin and eyes. In photosynthetic or­ ganisms, UV-B causes damage to DNA and alterations in 1. Theeffects of UV-B on aquatic bryophytes depend on the photosynthesis, growth and development. · species, and thus bryophytes do not constitute an homogene­ ous functional typewith respect to their responses to UV-B In the context of UV research, bryophytes may be interest­ (Martinez-Abaigar et al., 2003, 2004). Fontinalis antipyretica ing because they are structurally simple and lack structural is a relatively sensitive species and the exposed samples show defences against UV-B (hairs, thick cutides and epidermis). severe morphological and physiological alterations, whereas This could result in a higher UV-B sensitivity of bryophytes, ]ungermannia cordifolia is a relatively UV-B tolerant species as a group, in comparison with vascular . Bryophytes and it only shows a slight decrease in growth and the maxi­ from mountain streams are particularly exposed to the ef­ mum quantum yield of PSII (FJFm), together with DNA fects of UV-B radiation because UV-B increases with alti­ damage. The different sensitivity of both species could be tude and can easily reach organisms, given that they live at partly explained by the higher accumulation of UV-absorb­ relatively low depths. In addition, cold temperature limits ing compounds in the liverwort. metabolism and consequently the development of protecting mechanisms against UV-B, such as antioxidants, DNA re­ 2. The effects of UV-B on aquatic bryophytes depends not pairing systems, and synthesis of UV- absorbing compounds only on the species, but also on environmental fa ctors such (these compounds would act in a similar way to melanin in as temperature (Nuiiez-Olivera et al., 2004). The stressing humans) . effects of cold and UV-B may be additive in the UV-B-sensi­ tive Fontinalis antipyretica, given that low temperatures limit The vast majority of the research about the effects of UV-B the display of repair mechanisms. However, in]ungermannia on photosynthetic organisms has fo cused on terrestrial cul­ cordifoliathe interaction of cold and UV-B is less evident. We tivated plants and marine phytoplankton and macroalgae. also tested the interacting effect of cadmium and UV radia­ Bryophytes in general, and those from rivers and lakes in tion in this liverwort (Otero et al., 2006). Cadmium caused particular, have received much less attention. Because of the stronger stress than UV. Physiological damage was generally scarcity of studies and the controversial results fo und, our intensified by the combination of cadmium and UV, but this first objective is to increase our knowledge on the responses intensification depended on the variable considered. In these of bryophytes to UV-B radiation. Also, we are trying to elu­ cases when a great number ofvariables has to be analyzed, the cidate if bryophytes may be useful as bioindicators of the use of multivariate tools like Principal Components Analysis

35 Field Bryology number 91

may clarifY the effects of the different treatments and fac­ These can be the ecophysiological bases to establish in the fu­ tors. ture a bioindication net of the potential anthropogenic UV-B increase based on aquatic bryophytes. 3. The effects of UV-B on aquatic bryophytes depend not only on the species and the environmental factors, but also Acknowledgements on intraspecific differences depending for instance of the previous acclimation to sun or shade conditions (Nuiiez-01- Our thanks to the members of the Ecophysiology Group at ivera et al. , 2005). Shade samples were more UV-B-sensitive the University of La Rioja (Rafael To mas, Saul Otero, Nath­ than sun samples, but only in the UV-B-sensitive Fontinalis alie Beau court, and Maria Arr6niz-Crespo), and to the Span­ antipyretica, whereas in]ungermannia cordifoliathere was no ish Ministry of Education and Science, the FED ER fund, difference between both types of samples. and the Government of La Rioja fo r economic support.

4. In the field, the absorption spectra in the UV region of ten References and fo ur liverworts growing at 2000 m altitude were obtained (Arr6niz-Crespo et al., 2004). In the liverworts, Arroniz-Crespo M, NUiiez Olivera E, Martinez Abaigar high UV-absorbance and clearly hump-shaped spectra were J, Tomas R. 2004. A survey of the distribution of UV­ fo und, whereas low UV-absorbance and almost flat spectra absorbing compounds in aquatic bryophytes fr om a were generally fo und in the mosses. Thus, liverworts and mountain stream. Bryologist 107: 202-208. mosses may develop different protecting mechanisms against Arroniz-Crespo M, NUiiez Olivera E, Martinez AbaigarJ, UV-B radiation. Becker H, Scher J, Zapp J, Tomas R, Beaucourt N. 2006 (inpress) . Physiological changes and UV protection 5. Also in the field, 11 populations of ]ungermannia cordi­ in the aquatic liverwort fungermannia exsertifoliasubsp. folia growing along a natural altitudinal gradient of UV-B cordifoliaalong an altitudinal gradient ofUV-B radiation. from 1100 to 1800 m altitude showed considerable changes Functional PlantBiology. in their physiological variables, but only a few ones showed Martinez-AbaigarJ, NUiiez Olivera E, Tomas R, Beaucourt significant correlations with altitude (Arr6niz-Crespo et al., N, Garda-Alvaro A, Arroniz M. 2004. Daiios 2006). Among these, the global concentration of UV-ab­ macrosc6picos y microsc6picos causados par un aumento sorbing compounds increased with altitude, but only two de la radiaci6n ultravioleta-B en dos bri6fitos acuaticos out of five individual compounds were responsible fo r this del Parque Natural de Sierra Cebollera (La Rioja). Zubia increase: the new caffeic acid derivatives 5"-(7",8"-dihydrox­ 22: 143-163. ycoumaroyl)-2-caffeoylmalic acid and 5"-(7",8"-dihydroxy- Martinez-Abaigar J, NUiiez Olivera E, Beaucourt N, 7 -0-�-glucosyl-coumaroyl)-2-caffeoylmalic acid. These Garda-Alvaro A, Tomas R, Arroniz M. 2003. Different compounds may confer protection against UV-B, and thus physiological responses of two aquatic bryophytes to the liverwort would not be affected by the increasing UV­ enhanced ultraviolet-B radiation. journal ofBryology 25: B along the altitudinal gradient. In addition, the two new 17-30. compounds could be used as indicators of spatial changes NUiiez-OliveraE, Martinez-Abaigar J, Tomas R, Beaucourt in UV-B. Could they also be used as bioindicators of the N, Arroniz-Crespo M. 2004. Influence of temperature temporal changes in UV-B levels caused by anthropogenic on the effects of artificially enhanced UV-B radiation ozone depletion? on aquatic bryophytes under laboratory conditions. Photosynthetica 42: 201-212. 6. For bioindication purposes, adequate variables and species Nuiiez-Olivera E, Arroniz-Crespo M, Martinez-Ahaigar should be selected. Useful variables may be FviFm because J, Tomas R, Beaucourt N. 2005. Assessing the UV­ of its sensitivity, and UV-absorbing compounds and DNA B tolerance of sun and shade samples of two aquatic damage because of their specific response to UV-B. With bryophytes using short-term tests. Bryologist 108: 435- respect to UV-absorbing compounds, the measurement of 448. the concentration of individual compounds by HPLC has Otero S, Nuiiez-Olivera E, Martinez-Abaigar J, Tomas more physiological relevance than the usually employed R, Arr6niz-Crespo M, Beaucourt N. 2006. Effects of bulk UVabsorbance of methanolic extracts, given that cadmium and enhanced UVradiation on the physiology each compound may respond in a different manner to UV. and the concentration of UV-absorbing compounds of Among the species studied, ]ungermannia cordifolia is our the aquatic liverwort ]ungermannia exsertifolia subsp. most preferred species, and the concentration of its UV- ab­ cordifolia. Photochemical and Photobiological Sciences 5: sorbing compounds may be a promising bioindication tool. 760-769.

36 Reports ofBBS meetings

Mosses as bioindicators of nitrogen inputs in the environment 1•2Catherine Cooke, 1John Pearson, 2TimyMille r (1Un iversity College London, 2Rothamsted Research, Ha rpenden)

Anthropogenic nitrogen (N) deposition fr om burning fo ssil to test a hypothesis that Mnium hornum would be able to fuels, applying fe rtilisers and growing legumes has resulted sense changes in atmospheric N deposition, perhaps serving in an unnatural accumulation of N in atmospheric, terres­ as a useful bioindicator to measure changes in atmospheric trial and marine environments. Recent research, such as the N. This type of experiment had not been conducted before GANE (Global Nitrogen Enrichment) initiative, into N and after one month of fieldwork, Mnium hornum NRA and deposition effects has shown trends towards long-term envi­ tissue N03- concentrations recovered to levels fo und in the ronmental change. field at Mardley Heath.

Following on fr om research into the fo liar uptake and as­ Inputs from rainwater data revealed that critical loads fo r N similation of N in bryophytes the rapid initial induction of were almost reached on several occasions on the site during nitrate reductase activity (NRA) was investigated further that month however no detrimental effects to NRA or tis­ using inorganic-N in both Mnium hornum and sue N03- concentration accumulation were observed on the jimbriatum. From this work N-status models of both mosses N-starved mosses. It can be concluded that Mnium hornum were established over time. can serve as a good bioindicator of atmospheric N pollution ifNRA in vivo and tissue N03- concentrations are measured Mnium hornum had a tremendous capacity to sustain itself in conjunction with one another. Living bioindicators also with NRA being induced and N03- stored long term even have the advantage of detecting interactions between envi­ whilst undergoing N starvation. This moss was then used ronmental pollutants in this way.

Cryopreservation - a tool fo r conservation JK Rowntree (R oyal Botanic Gardens, Kew, Surrey)

Since 2000, the Micropropagation Unit at the Royal Botanic diverse ecological requirements. Recovery rates using a sin­ Gardens Kew has been host to a project funded jointly by gle protocol have been high, ranging from 68-100%. This English Nature, Scottish Natural Heritage and the Coun­ is unusual and is attributed, in part, to the totipotency of tryside Council for Wales for the ex situ conservation of bryophytic material (ability to regenerate whole plants from threatened UK bryophytes. One of the aims of the project a single cell) and the inherent ability of bryophytes to over­ has been the development of methods for the long term stor­ come physiological stress. To date, twenty species of moss age ofbryophyte material via cryopreservation; the storage of and one species ofliverwort with threatened status in the UK living tissue at -196°C in liquid nitrogen. A relatively simple have been successfullyfr ozen. These are currently being held encapsulation-dehydration protocol has been developed and in the cryopreserved collection at Kew. tested on gametophytic material from a range of species with

Recent changes in the Cornishbryophyte floraand their causes David T. Ho lyoak (Camborne, Cornwall)

A project to record distribution of bryophytes in Cornwall fr om which detailed notes have now allowed most records to and the has been underway since 1993, with be assigned to tetrads. over 77,000 records amassed by 2006. Recording is being carried out by tetrads (the 2 x 2 km squares of the National Detailed quantitative analyses of changes in the bryoflora Grid) . By 2006 good coverage at this scale had been obtained are planned when fuller coverage of East Cornwall has been in We st Cornwall (v.-c. 1), with data fo r >95% of tetrads, but achieved. In the meantime it is already apparent that there there is still only patchy coverage of East Cornwall (v.-c. 2). have been some large changes between the 1960s and the Comparisons can be made with results of intensive surveys 1993-2006 period, with serious implications fo r conserva­ carried out by Mrs Jean A. Paton mainly during 1960-1968, tion of some of the rarer bryophytes. Changes in land-use

37 Field Bryology number 91 have had the greatest impacts, principally through abandon­ of the heath land vegetation on Bodmin Moor but it keeps ment of marginal land. This has involved cessation of graz­ many of the valley bogs open. Current efforts by conser­ ing on coasts and total neglect of much old mining ground, vationists to reduce grazing pressure will probably result in resulting in many fo rmerly open habitats being replaced by recovery of some of the heather moorland, but lead to devel­ scrub. Conversely, agricultural intensification has occurred opment of tall Molinia stands that will reduce the bryophyte on higher ground of Bodmin Moor and the West Penwith interest of mires. moors, with drainage, fe rtiliser inputs and overgrazing of grasslands, resulting in loss or damage to mires, flushes and Compared to the effects of land-use changes, the impacts on wet heathland. the bryoflora of invasive alien species, pollution or climatic change seem relatively minor. The only alien bryophyte that Reduction of open habitats around the coasts has led to de­ has become widespread and locally abundant is Campylopus clines in several Fossombronia and Riccia species, including introjlexus, which now blankets much open soil in heathland such rarities as F. crozalsii, F. maritima, R. biforca and R. and on clifftops that might previously have supported other nigrella. Mosses of open coastal habitats have also declined, species. In the Isles of Scilly the aliens Lophocolea bispinosa with some rarities badly affected, notably Tortula canescens, T and L. semiteres are also colonising much open ground and cuneifoliaand T wilsonii. Weissia multicapsularis has declined both are now established on the mainland, the fo rmer now both inland and on the coasts, with the two small popula­ occurring extensively on areas of open china-day spoil. tions surviving on the south coast of East Cornwall now be­ ing all that are known worldwide. Despite officialprotection Possible effects of recent climatic warming have been much of some of the best areas, metalliferous mine sites are also discussed, but they are not as yet striking in the bryoflora as a sufferingfr om increased scrub growth, even where over-graz­ whole. Several species newly recorded in Cornwall are south­ ing also occurs close by such as at Phoenix United Mine. ern thermophiles (e.g. Bryum valparaisense, Grimmia crinita Declining rarities on metalliferous sites include Cephaloziella and the rapidly spreading Didymodon umbrosus and Semato­ massalongi, C. nicholsonii, Pohlia andalusica and Scopelophila phyllum substrumulosum) but others are not (e. g. Didymodon cataractae. Mining effectively ceased in Cornwall many years tomaculosus, Distichium inclinatum, Grimmia hartmannii, ago, so that continuing declines of bryophytes requiring G. orbicularis, and Plagiothecium cavifolium) . The clearest open mine-spoil habitats will be ineviteable unless habitats evidence ofbryophytes responding to a warmer climate may are kept open by deliberate conservation management work. come from Cololejeunea minutissima and Colura calyptrifolia, two small thermophilous liverworts that have ranges extend­ Agricultural 'improvement' of the Cornish moors has been ing into the tropics. Both of these have increased greatly in in progress since the nineteenth century but it has tended Cornwall since the 1960s, when both were essentially coastal to accelerate in the past few decades. Mechanical diggers and the latter was known only on the Lizard peninsula. By now reduce the difficulties of draining wet ground, and ar­ 2000 both had colonised large areas inland, including high tificial fe rtilisers are more easily spread over hill grasslands ground on Bodmin Moor where there is no doubt they were and heath, causing eutrophication of mires downslope. Since absent in the 1960s. the 1960s the West Penwith moors have lost many of their sites for Sphagnumsp p., but they remain unharmed on some Causes of the changing abundance of several species remain parts of Bodmin Moor. Flush bryophytes have sustained uncertain. Several mosses that grow on open acidic rock sur­ great losses throughout Cornwall, especially those that were faces have declined since the 1960s, this being especially ob­ always scarce plants here because they require some base en­ vious with Andreaea rothii and Racomitriumfosciculare, both richment, such as Calliergon sarmentosum and Scorpidium of which are now very rare in We st Cornwall even on the scorpioides. Splachnum ampullaceum appears to have become superficially undamaged rockyareas of the Land's End penin­ extinct since the 1960s, presumably due to Ivermectins used sula. Atmospheric sulphur pollution originating from ship­ as veterinary wormers reducing populations of the dung flies ping may have affected them, as might climatic warming. that disperse its spores. Over-grazing now threatens much

38 Reports of BBS meetings

Mosses and the African Plants Initiative: digitisation at the Natural History Museum, London Jo Wi lbraham (Natural History Museum, London}

The African Plants Initiative (API) is an international col­ Scanning specimens- The specimens are scanned using an in­ laborative project to create an online database of herbarium verted Epson 10,000 XL Expression Flatbed Scanner. The specimen images and associated data, contributed by partner specimen sheet is placed on a platform that is raised up to herbaria and funded by the Andrew Mellon Foundation in the inverted scanner and scanned at 600 dpi, producing an New Yo rk. The Natural History Museum (NHM) received image of approximately 200MB. Scanning specimens is pref­ funding in autumn 2005 to digitise the collection of moss erable to photography as the latter leads to problems with type specimens from Mrica and Madagascar (liverworts and resolution and extensive lighting requirements. hornworts are not included in this project). The NHM her­ barium holds approximately 25,000 moss type specimens, Associated label information - Specimen label information is 4,000 of which are from Mr ica and will be entered into the recorded into a database and this data, along with the speci­ API database. The API website is set to launch in February men images, is exported to the API administrative headquar­ 2007 and is going to be available to institutions by subscrip­ ters in New Yo rk. tion. The subscription rates will work on a sliding scale to ensure affordabilityfo r partner institutions in Mrica. Targets -The NHM has pledged to digitise 4,000 moss speci­ mens in one year. We are now nearing the end of this project Themoss herbarium at the NHM and are currently on target. (With this reckoning we could digitise the entire moss herbarium of approximately 800,000 Theherbarium is a vast store of information about plant di­ specimens in only 200 years!). versity and systematics. For many parts of Mrica large num­ bers of allegedly endemic taxa have been described, often Additional API activitiesat the NHM with poorly defined characters, and there are few floristicac­ counts ofbryophytes. Identification ofbryophyte collections Brian O'Shea has produced a complete checklist of moss may have to be made using only original descriptions (often names fo r Sub-Saharan Mrica. This includes all current published in obscure journals) and in some cases the type names, synonymy and nomen nudum. The checklist will specimen is the only known collection. The type specimen is be incorporated into the API website and a version will be the singular entity on which the name of a plant is based and downloadable as a Tr opical Bryology Report. A searchable access to these specimens is imperative fo r taxonomic work. database, recording bibliographic information about plant Information on the location and condition of type specimens collectors in Mrica, is also being produced at the NHM. is oftenhard to findand thus creates an impediment to taxo­ This data will be available through the API website and also nomic study. through the museum in the near future.

Digitisationmeth odology Thefuture

Type validation - As not all type specimens are marked up The next fo cus for this digitisation project is Latin America. as such in the collections, some experience and a substantial Estimates suggest that the herbarium holds approximately library are required to identifY original material. It has been 8,000 moss type specimens from Index Muscorum regions necessary to work through all the fo lders of Mrican speci­ 'America 2-6', and the digitisation of these will be under­ mens to locate type material though the time restrictions of taken in a two-year project. The specimen images produced the project limit the extent to which nomenclatural research by the NHM fo r the API project will remain the property of can be undertaken. the museum and will be available for use in futureprojects to increase accessibility to the collections.

39 Field Bryology number 91

Are urban bryophytes boring? Results fromKing's Lynn Robin Stevenson (Ki ng's Lynn} and Ma rk Hill (CEH Mo nks Wood}

Urban bryophytes have been investigated by many research­ Results show that several of the hypotheses are justifiedwhen ers, especially on the European continent. In Britain, the applied to the town centre, but are not true of the suburban most significant studies by Gilbert (1968, 1970, 1971) date areas that surround it. In particular, the overall magnitude of from a time when air pollution was at its maximum. Reinva­ the flora wasexceptionally large for East Anglia. Thisresult sion of epiphytes was noted in London as early as 1989 (Ad­ can be explained in part by the fact that ancient woodland ams & Preston, 1992) and is now recognized as a widespread is encapsulated within suburban King's Lynn and also by the phenomenon, in the countryside as well as in towns. presence of adjoining arable land. Our preliminary conclu­ sion is that the town has added to local species richness by There has hitherto been no systematic survey of the bryo­ providing a range of urban habitats while having apparently phytes of a British town, so that it is impossible to docu­ litrle effecton adjacent woods and fields. ment change with any certainty. Indeed, the nature of ur­ ban bryophyte floras is not clear. To make a start with this References problem, RS made a systematic survey of the bryophytes of King's Lynn, a medieval town with about 41,000 inhabitants Adams KJ, Preston CD. 1992. Resources fo r documenting near the mouth of the Great Ouse river in East Anglia. A changes in species and habitats. In: Harding PT, ed. square 5 km x 5 km was studied. This included almost all Biological recording ofchanges in British wildlife.London: urban and suburban parts of the town, together with some HMSO, p 31-43. surrounding countryside. Each 1 km square was visited on GilbertOL. 1968. Bryophytes as indicators of air pollution several occasions between 1999 and 2004, and its bryophytes in the Tyne valley. New Phytologist 67: 15-30. were enumerated. Gilbert OL. 1970. A biological scale for the estimation of sulphur dioxide pollution. New Phytologist 69: 629-634. The bryophyte floracomprised 151 species, and its composi­ GilbertOL. 1971. Urban bryophyte communities in north­ tion was tested against a set of hypotheses about urban bryo­ east England. Transactionsof the British Bryological Society phytes that have resulted fr om studies in continental Europe. 6: 306-316.

Saying goodbye to our Arctic? Thefuture of snowbed vegetation in Scodand Cordon Rothero (Argyll}

Bryophyte dominated snowbed vegetation is one of the rar­ massif and the Ben Alder area where snowbeds are frequent. est habitats in the UK (probably restricted to less than 1000 In addition to these core areas, there are a number of other hectares) and intuitively it must be the habitat most threat­ mountains with smaller snowbeds, the most important of ened by climate change. There are various types of snowbed which is probably Creag Meaghaidh but the list also includes vegetation in Scotland but here the term refers to those types Ben Lawers, the Affric hills and stretches north to Ben Wyvis where lower plants are dominant. In terms of the national and Beinn Dearg. There are broadly two sorts of snowbed. vegetation classificationthis essentially means U11 (the Pol:y­ The most widespread are those in deep coires with craggy trichum sexangulare - Kiaeria starkei snowbed) and U12 (Sa­ headwalls and block scree, typified by sites in the Ben Nevis fix herbace a - Racomitrium heterostichum snowbed) . I am massif. The other type of snowbed has a lesser amplitude of not particularly happy with U12 which included a number relief and finer substrates and such snowbeds are typicalof the of stands with Salix herbacea which are not particularly sites on the Cairngorm plateau. Obviously, there are many chionophilous and prefer, naturally enough, to use the as­ sites which combine some fe atures of both these types. sociation I described in my survey in 1989-90, the Marsu­ pella brevissima- Anthelia juratzkana snowbed, often termed How do they fo rm? Fallen snow doesn't stay put - it is the 'hepatic crust'. In addition the Pohli a ludwigii snowbed blown about by the wind and deposited on lee slopes in hol­ community I described should also be included, plus the as­ lows, along 'cornice lines' and in coires, often to prodigious sociated meltwater springs and flushes. depths. It is worthwhile pondering the fact that winds can reach 275 kmh on Cairngorm, giving a lot of energy to shift Where do these snowbeds occur? The distribution picks out snow. With the prevailing winds being SW to W, many the higher hills, particularly the Cairngorms, the Ben Nevis of these accumulations are on slopes facing N round to E,

40 Reports ofBBS meetings slopes where insolation will be relatively low even in high More systematic surveys of snow patches have been made summer. This means that melting is reduced and the snow by Adam Watson of the Centre fo r Ecology and Hydrology patches persist, often into August and, in most years, some (CEH) at Banchory for the past 10 years but this is not long snow persists throughout the year. The fo rmation of snow enough to give any kind of pattern. No snow patches per­ patches and their size is critically dependant on the extent of sisted through the summer to the next winter snows in 2003 the catchment area, the area from which snow can be scoured and only one and two small patches persisted in 2004 and - this is why the high plateaux of the Cairngorms and the 2005 respectively, although in 2005 I saw a patch on Aonach Alder Forest are so important. Because the winds and to­ Mor that was lOOm long and 40m wide in late July. pography are fairly stable, snow patches tend to fo rm in the same places with the same pattern of melting year afteryear The UKClimate Impact Programme (UKCIP) has published with resultant effects on the vegetation. The short snow-free fo ur alternative scenarios fo r change, which are essentially season means that vascular plants struggle to persist and the 'what-ifs' rather than predictions, but we can be certain that competitive advantage is with bryophytes and lichens. there will be change. Theexact pattern may depend on such variables as the cooling effect of any slowing of the North What interesting plants do we stand to lose? There are a Atlantic Drift. In the higher hills temperatures may be up by number of species which have all or most of their British 1 ac by 2020 and by 2°C by 2050 but some models predict sites in snowbeds. Some of them, like Polytrichumsexan gu­ that the degree of warming may be higher in the winter. All lare, Kiaeriafolcata, Kiaeriastarkei and Marsupella brevissima fo ur scenarios envisage an increase in winter precipitation of are common to virtually all snow beds and often fo rm large some 10% in the Cairngorms but this is offset by a decrease stands. Most of the better sites will also have species like in summer precipitation so that total precipitation remains Moerckia blyttii, Pleurocladula albescens, Marsupella conden­ within the bounds of normal variation. sata and Andreaea nivalis, the latter sometimes in remarkable abundance. There are a number of extreme rarities associated Predicting the effect of these sorts of changes on snow patches with the snowbeds. Marsupella arctica has only two sites in is difficult. Increase in winter precipitation, at least initially; Scotland, its only sites south of the Arctic. Marsupella sparsi­ may mean greater snowfall to fe ed the snow patches but, as foliaand Gymnomitrion apiculatumalso have only a handful the proportion of winter precipitation falling as rain increas­ of sites, usually with small populations, although both can be es, snow patches could take a double whammy -less drifting very hard to pick out in the field. Andreaea blyttiiis some­ snow and more melting between snow falls. There are other what more widespread but two rather more enigmatic An­ complexities - future winds are difficult to predict but the dreaea species (Andreaea alpestris and Andreaea sinuosa) seem suggestion is that they will be somewhat stronger and so will to be more restricted. The flushes and mire areas associated shift more snow into the snow patch areas. How quickly with snowmelt also have their special species. Theyare often falling snow accumulates and how long it persists are also picked out by large stands of Pohlia wahlenbergii var. glacialis affected by the temperature of the underlying soils, rocks and and may have cushions of Scapania paludosa associated with gravels and this can be critically affected by early frosts when them and occasionally Sphagnum riparium and S. lindbergii. the ground is snow-free. The durability of the snow-pack is also affected by the process of partial melting and re-freezing. What of the future? There is some evidence that change is On a brighter note - what melts snow patches in the summer already taking place in the hills. There has been a 0.4°C in­ is not hot sunshine but warm rain and a decrease in summer crease in temperature in Scotland since late 1960s; in these precipitation may mitigate things a bit. higher latitudes minimum temperatures have risen faster than maximum (+0.2oC and +O.loC per decade, respectively) . In Hard evidence of change in the snow bed vegetation is lack­ the Cairngorms, comparison of mean monthly precipitation ing and casual observation suggests that the extent of the veg­ between 1941-1970 and 1961-1990 show some seasonal etation now is little changed from that which I observed in alterations, with a decrease in summer rainfall by 10-15% 1989 and 1990. This is particularly true of the plateau type and an increase in winter precipitation of 5-l 0%. The effect snowbed, typical of the Cairngorms, but some of the coire on snow patches is rather more difficult to interpret but the sites look to have a greater cover of vascular plants. Dem­ general impression, certainly since the 1980s, is of fewer and onstrating change in the vegetation will require a long term smaller areas of snow persisting on the hills at the beginning monitoring programme and this is currently being planned. of summer and some evidence from the Braemar area sug­ It is hoped that this programme will attract significant fund­ gests that this trend was also apparent in the 1950s and 60s. ing from Scottish Natural Heritage.

41 FieldBryo logy number 91

Changing distributions in a changing world Fred Rumsey (Na turalHisto ryMu seum, London)

The dynamic nature of distributions is rarely acknowledged. is clearly untrue of bryophyres and the fo rmer assumes that Bryophyre distributions may be static; species persist through the environment in which species occur is essentially stable. their precise adaptation to particular niches and indefinite Changing environmental and climatic factors can be corre­ life-spans and fail to spread more widely usually through re­ lated with the increase shown by some groups of species, e. g. productive incompetence. In an unchanged world we might epiphyres such as Orthotrichumspp ., Cryphaea, various small have greater expectation fo r distributions at anything but Lejeuneoid hepatics, which from reproductive strategy and the finest scale to remain essentially unchanged. Webb when ecology we might expect to be rapid responders. While there considering criteria fo r presuming native status of vascular are a few genuine examples of alien bryophyre introductions plants made a noticeable increase in range/numbers pre­ many more examples of native increasers, or natural colonists sumptive evidence fo r alien status but then he also regarded have, I believe, been too hastily considered alien. the lack of sexual reproduction in a similar light. The latter

Conversazione posters Atherton, I (Hampshire). BBS Field Guide displays. Stieperaere, H (National Botanic Garden, Belgium) & Mat- cham, H (London). Three Notothylas species in Central M­ Potter, PR (University of Hertfordshire) . Moss growth on a rica and Uganda. temperate glacier: Falljokull, Iceland.

Field excursion to FlitwickMoor, Bedfordshire, 10 September 2006 AlanOuten (Bed fordshire)

I have to confess that when I was asked to suggest some pos­ the most important natural history sites in south-east England sible sites fo r the field meeting to follow the 2006 AGM I and has been long recognised as important fo r its bryophyre hoped very much that Flitwick Moor in Bedfordshire would flora. James Saunders did much collecting here in the 1880s, be the chosen venue! and To m Laflin and Peter Taylor in the late 1940s to early 1950s. The Cambridge Botany School with Harold White­ Flitwick Moor is a Site of Special Scientific Interest (SSSI) house made several excursions here in the 1960s and 70s and and a reserve of the Beds & Cambs Wildlife Tr ust, compris­ my own studies here began in 1970. With a bryophyre list ing 31 ha of acid mire, fen, open water, acidic and neutral of 113 species including ten species of Sphagna, Flitwick grasslands, alder carr and oak/birch woodland. It is partic­ Moor has often been described as the richest bryological site ularly important because the unusual flow of groundwater in south-east England. (To put this in context Wicken Fen in through the greensand under the reserve has produced a Cambridgeshire has a total of 110 recorded bryophyre spe­ range of acidic and neutral habitats in a very small area. Peat cies but is eight times the size of Flitwick Moor) . was extracted until the rnid-1950s and used mainly in purify­ ing gas. Water from the Chalybeate springs rich in iron was Over twenty members of the Society from across Britain once bottled and sold as a blood tonic. The pressures on the and from as far away as Belgium attended the fieldmeeting. site fr om surrounding farmland and fromwater extraction by The visit proved to be exceedingly productive and has added water companies are now further exacerbated by attempts to greatly to the knowledge of this site and further emphasised obtain planning permission to build housing on the adjacent its importance. No fewer than 83 different species were ob­ field. served during the day but remarkably 22 of these were addi­ tions to the list for the site. Four species and one variety were Its rich biodiversity means that this is without doubt one of also new fo r the County and one confirms an old record.

42 Reports of BBS meetings

Many of the additions were of epiphytes reflecting their re­ striatum, lfylocomniumspl endens, Hy pnum resupinatum, Iso­ covery across SE England. thecium myosuroides (fo und by Mark Lawley) , Orthotrichum affi ne (found in at least 15 different places!), O.lyelli, Polytri­ Sphagnum palustrevar. palustre is not uncommon here but chum longisetum (determined by Mark Hill), PseudotttXiphyl­ Mark Hill also identified Sphagnum palustre var. centrale, lum elegans, Rhynchostegium confertum, R. riparioides, Chilo­ otherwise currently known from one other site in Britain. scyphus pallescens, Metzgeriaforcata and Pellia endiviifolia. To m Blocked added fo ur species to the County list, these being Eurhynchium speciosum, Ulota bruchii, Metzgeriafru ­ The overall list for the site therefore now stands at 109 moss­ ticulosa and Cololejeunea minutissima. He also fo und Orthot­ es and 26 Hepatics, an overall total of 135 species. Forty-nine richum tenellum (the first Bedfordshire record since 1892). species of fungi were also recorded during the day of which Richard Fisk collected Ulo ta phyllantha, (a species with just fo ur were additions to the site list. one other known Bedfordshire site). My thanks to all those who contributed records making this Other additions to the site list were Bryum moravicum, such a successful event. Cryphaea heteromalla, Didymodon sinuosus, Eurhynchium

Summer Field Meeting in East Sutherland,July 1 st_gth

2006

Mark Lawley

12A Castleview Terrace, Ludlow, Shropshire SY8 2NG

"Theysay that time c. 1 07) , and disappeared into a variety of hotels, Heals a broken heart. " guest-houses, and self-catering accommodation. the old song goes, Along with unbroken fine weather throughout ''Buttime has stood still the week, this mixture of lodgings contributed Since we Jell ap art. in large measure to the pleasure of our holiday, I can'tst op loving you .... " fo r the advantages of roomy self-catering accom­ modation again became evident, just as they had Most English botanists feel this way about the two summers previously in North Aberdeenshire. Scottish Highlands, fo r absence and distance ever Some members set up their microscopes in the make the heart grow fo nder. We yearn fo r the drawing room in order to determine their gather­ fr eedom of wild open spaces, and as car-bonnets ings comfortably and in companionable circum­ pointed north at the beginning of July, our spirits stances during the evenings after each day's excur­ rose with the barometer, in anticipation of adven­ sions, while those of us less allured by the prospect tures coming our way. of work sank into the lounge's soft settees with a cup of tea and planned the morrow's outings. Nearly twenty bryologists descended on the coastal village of Golspie in East Sutherland (v.- Our domestic arrangements also allowed Rexibil-

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