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Abstract. Different measures of species abundance, particularly cover and biomass, are often used as if they were interchangeable. We ask to what extent the measure of abundance affects conclusions reached in plant community ecology. The test data comprised 35 plots, each 1 m × 1 m, on serpentine vegetation in Tuscany, Italy, in which both cover and biomass were measured. The measure of abundance used made rather little difference when plots were examined in terms of the rank abundance of the species present, and little difference to the results of a DCA‐ordination. Likewise, species showed similar variation across plots in cover as in biomass. In calculating species diversity, agreement between measures of abundance was lower, but still good. For evenness, the correlation between cover and biomass results was lower again, though more so with some indices than with others. For the shape of the RAD (Relative Abundance Distribution), cover and biomass gave quite different results, the Zipf‐Mandelbrot RAD model most commonly giving the best fit to the cover data, but the General lognormal model to the biomass data. These tendencies can be related to the intrinsic characteristics of cover and biomass as measures of abundance. The parameters of the model fits also differed between abundance measures. We conclude that the importance of using biomass as the measure of abundance depends on the ecological feature being examined. The difference between the two measures may be greater in other vegetation; very little information is available. In the current state of knowledge it is dangerous to use another measure as a surrogate for biomass.

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Fungi are a hyperdiverse taxonomic group that may be disappearing at a very high rate. Identifying fungal species is difficult in the field, and the use of highly specialized taxonomists is required. Data and expertise on vascular plants are, on the other hand, much more common and easy to find. We tested the potential of using vascular plants as surrogates to select reserve sites that maximize the pooled number of fungal species. We used data from 25 forest plots in Tuscany, Italy, that were sampled for woody plants, all other plants, and fungi. Species richness of woody plants and all other plants did not correlate with species richness of fungi. The gradients in species composition were similar among the three considered groups, as indicated by a detrended correspondence analysis ordination and species complementarity between pairs of plots. Fungal communities of the 25 plots had a lower β diversity than plant communities, and there were no pairs of totally complementary sites. Site prioritization for conservation was obtained through integer linear programming to find for any given number of sites those combinations containing the maximum pooled species richness of woody plants or all plants. The combinations of sites obtained by optimizing vascular plant species did not maximize the pooled species richness of fungi, whereas those obtained by maximizing woody plant species provided better results for sets of four to eight plots, but not for all the possible combinations. These results indicated that, in general, vascular plants cannot be used to maximize fungal species richness. Utilización de Plantas Vasculares como un Taxón Sustituto para Maximizar la Riqueza de Especies de Hongos en el Diseño de ReservasResumen: Los hongos son un grupo taxonómico hiperdiverso que posiblemente este desapareciendo a una velocidad muy alta. La identificación de especies de hongos en el campo es difícil, y se requiere el uso de taxónomos muy especializados. Por otra parte, los datos y pericia con plantas vasculares son mucho más comunes y fáciles de encontrar. Probamos el potencial del uso de plantas vasculares como sustitutos para seleccionar sitios de reserva que maximicen el número de especies de hongos. Utilizamos datos de 25 parcelas en bosques de Toscana, Italia, en las que muestreamos plantas leñosas, todas las demás plantas y hongos. La riqueza de especies de plantas leñosas y demás plantas no se correlacionó con la riqueza de especies de hongos. Los gradientes de composición de especies fueron similares entre los tres grupos considerados, como lo indica una ordenación de análisis de correspondencia sin tendencia (DCA) y la complementariedad de especies entre pares de parcelas. Las comunidades de hongos de las 25 parcelas tenían una diversidad beta menor a la de comunidades de plantas, y no hubo pares de sitios totalmente complementarios. La priorización de sitios para conservación se obtuvo mediante programación lineal integral para encontrar un número determinado de sitios cuyas combinaciones contengan la máxima comb...

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The present study evaluates the relative importance of environmental factors in affecting the species composition and abundance of the plant communities on ultramafic soils in Tuscany, Italy. We used rigorous sampling techniques to test hypotheses generated from exploratory studies performed previously. Vegetation–environmental relationships were analyzed using 50 plots, each 1 m2, randomly located throughout a 22‐ha area in the Upper Tiber Valley. We confirm that the exchangeable fraction of nickel in the soil is almost never high enough to affect the vegetation. However, physical factors (e.g. substrate setting and elevation) are important in controlling the distribution of plant species. Tree cover (almost exclusively due to the introduced plantation pines) also had a significant affect on the vegetation composition and on soil features such as the C/N ratio. Other important factors significantly related to the gradients in vegetation composition (e.g. rockiness and total soil nitrogen) are interpreted as factors related to the vegetation composition through a positive feedback mechanism.

The influence of agriculture, i.e., of fertilizers and ammonia emissions from crops and sheep grazing, on epiphytic lichen vegetation, and the use of nitrophytic lichen species in bioindication of air pollution were investigated in a geothermal area in central Italy. Floristic analysis showed that the lichen vegetation is only slightly influenced by agriculture. Analysis of the lichen data and chemico-physical parameters of tree bark supporting lichen growth failed to demonstrate marked differences between agricultural and non-agricultural sites, the higher total frequency of nitrophytic species in agricultural sites being the only parameter discriminating between the two site types. Bark nitrogen and pH were not discriminant. Factors determining the higher total frequency of nitrophytic species in agricultural sites may include dust impregnation of bark and the drier microclimate of trees in these sites. It is concluded that nitrophytic lichens can be included in the calculation of the Index of Atmospheric Purity in the study area.