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AGM and Bryological Symposium 2006, Hatfield 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 bryophytes 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, Scotland, Wales Alan Outen whose account of the excursion can and two from mainland Europe. 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 bryophyte shoots), and growth. We have studied mainly since 1980). It is estimated that a 1 o/o ozone loss causes a two species: the moss 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 plants. 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 mosses 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
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