Abstract:The epiphytic lichen vegetation of a heavily grazed Mediterranean mixed evergreen sclerophyllous and deciduous shrubland was studied. Differences in the epiphytic lichen vegetation seem to be largely determined by changes in the architecture of the bushes as well as by the differences in the space between them. In some cases, despite grazing pressure, the epiphytic lichen vegetation does not change dramatically.
“…Detecting the effect of climate change in arid areas is complicated by several environmental factors, including background air pollution and eutrophication from animal grazing (Pirintsos and Loppi 2003;Pirintsos et al 1998). The experimental design adopted in the present study aimed at detecting responses induced by a regional climatic gradient and at reducing the noise of other disturbances that make difficult attributing an observed change to a specific cause (Insarov and Schroeter 2002).…”
Section: Detecting Responses To a Climatic Stress In Arid Environmentsmentioning
A climatic change was simulated transplanting samples of the lichens Evernia prunastri (L.) Ach. and Pseudevernia furfuracea (L.) Zopf v. furfuracea along a 1,400 m altitudinal gradient in the northern side of the island of Crete (Greece). The working hypothesis was that the photosynthetic performance (i.e. pigment content, chlorophyll degradation and photosynthetic efficiency) of transplanted lichens varies along the altitudinal gradient. The overall effect observed was a general depression of the photosynthetic performance along the gradient. Concentrations of chlorophyll a, chlorophyll b and carotenoids decreased with decreasing elevation and along with the hottest and driest months of the year, with chlorophyll b being the most sensitive parameter to dry conditions. Chlorophyll degradation decreased with increasing elevation. The exposure period was the main factor affecting photosynthetic efficiency, with lower values during summer months. We argued that the water content of lichen thalli is the most important factor determining differences in photosynthesis under the experimental conditions. This allowed to suggest that the lichen photosynthetic performance deserves further investigation as early biological indicator of atmospheric stress induced by dry conditions and, to a greater extent, for the assessment of the desertification risk in the arid Mediterranean environment.
“…Detecting the effect of climate change in arid areas is complicated by several environmental factors, including background air pollution and eutrophication from animal grazing (Pirintsos and Loppi 2003;Pirintsos et al 1998). The experimental design adopted in the present study aimed at detecting responses induced by a regional climatic gradient and at reducing the noise of other disturbances that make difficult attributing an observed change to a specific cause (Insarov and Schroeter 2002).…”
Section: Detecting Responses To a Climatic Stress In Arid Environmentsmentioning
A climatic change was simulated transplanting samples of the lichens Evernia prunastri (L.) Ach. and Pseudevernia furfuracea (L.) Zopf v. furfuracea along a 1,400 m altitudinal gradient in the northern side of the island of Crete (Greece). The working hypothesis was that the photosynthetic performance (i.e. pigment content, chlorophyll degradation and photosynthetic efficiency) of transplanted lichens varies along the altitudinal gradient. The overall effect observed was a general depression of the photosynthetic performance along the gradient. Concentrations of chlorophyll a, chlorophyll b and carotenoids decreased with decreasing elevation and along with the hottest and driest months of the year, with chlorophyll b being the most sensitive parameter to dry conditions. Chlorophyll degradation decreased with increasing elevation. The exposure period was the main factor affecting photosynthetic efficiency, with lower values during summer months. We argued that the water content of lichen thalli is the most important factor determining differences in photosynthesis under the experimental conditions. This allowed to suggest that the lichen photosynthetic performance deserves further investigation as early biological indicator of atmospheric stress induced by dry conditions and, to a greater extent, for the assessment of the desertification risk in the arid Mediterranean environment.
“…3). According to Loppi & De Dominicis (1996), Loppi et al (1998), Pirintsos et al (1998) the xeric conditions and rural-agricultural environment indirectly support dust impregnation of the bark and the drier microclimate of trees in the Mediterranean area, enhancing xero-nitrophytic lichen species diffusion. In our survey area, where for the above mentioned reasons fruticose and meso-acidophytic foliose sensitive species (Barkman, 1958) were lacking, the sampled flora was mainly composed by crustose growth forms (62%), while the remaining part was dominated by narrow-lobe foliose species.…”
Section: Evaluation Of Lichen Diversity Valuesmentioning
Abstract:The results of a bioindication study based on the diversity of epiphytic lichens in a semi-arid area of South Italy are presented. The area features the presence of an industrial zone located in a rural context. The survey was performed in 20 sampling sites. The lichen diversity values (LDV) were determined by the frequencies of all lichen species within a sampling grid placed on tree trunks. Lichens demonstrated a condition of environmental alteration extending to the industrial zone, and tending towards a recovery in the rural surroundings. The survey also showed evidence of eutrophication all over the study area.
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