Ies, and associated photoautotrophs. Environmental conditions in the kind locality: Discharge (L s-1): 3.five, Temperature

Ies, and associated photoautotrophs. Environmental conditions in the kind locality: Discharge (L s-1): 3.five, Temperature ( C): 5.three, conductivity ( cm-1): 62, alkalinity ( q L-1): 311, pH: six.six, nitrate (mg L-1): 1.two, TP ( L-1): 7 (see [1] for more details). As issues photoautotrophs, within this incredibly shaded source the competitive balance involving huge groups (algae, lichens, bryophytes, and vascular plants) is clearly favorable for the mosses, which cover virtually all of the lithic substrata [dominance of Brachythecium rivulare W.P. Schimper, each submerged and, in significant portions, emerged, and also a particular relevance of Plagiomnium undulatum (Hedw.) T.J. Kop. and Rhizomnium punctatum (Hook.) T.J. Kop.]. Vascular plants aren’t abundant (as cover), and Adenostyles glabra (Miller) DC. and Saxifraga rotundifolia L. may be talked about among them. In terms of cover, bryophytes are followed by lichens. These involve two species which are hardly ever reported in Italy: Verrucaria madida Orange, an amphibious species in frequently flooded web pages on siliceous rocks, frequently in association with other aquatic lichens and bryophytes, and Verrucaria aquatilis Mudd., typical both in springs and along streams, in conditions of perennial/frequent submersion. Benthic macroalgae are uncommon and mainly represented by the red freshwater alga Hildenbrandia rivularis (Liebmann) J. Agardh, which can be characteristic of shaded springs with well-buffered waters and medium-high conductivity. The key co-occurring diatom species at the kind locality (at the least 5 relative abundance in one of the slides): Achnanthidium minutissimum sp. gr., Amphora inariensis Krammer, Amphora indistincta Levkov, Brachysira exilis (K z.) Round and D.G.Mann Cocconeis pseu-Diversity 2021, 13,eight ofDiversity 2021, 13,Sulphates (mg L-1) Cl-1 (mg L-1) TN ( L-1) SRP ( L-1) Mn ( L-1) Zn ( L-1)dolineata (Geitler) Lange-Bert., Gomphonema elegantissimum E.Reichardt and Lange-Bert., Humidophila perpusilla (Grunow) Lowe, Kociolek, J.R.Johansen, Van de Vijver, Lange-Bert. 9 of 20 and Kopalov Planothidium angustilanceolatum sp. nov., P. frequentissimum (Lange-Bert.) Lange-Bert., P. lanceolatum, Psammothidium grischunum Bukht. and Round. Ecology (Table 1, Figure 3a). With reference to temperature, E. Bentiromide Formula crassiminor includes a reduce optimum weighted average than E. minor (Table 1); consistently, E. crassiminor -11 five.1 1.4 11.five 2.2 1.four 4.3 -7.39 1.45 10 also appears 0.4prefer sites0.2 to which are much more shaded (Figure 3b). As issues pH2.28 10-5 (Figure 3e), 1.7 0.eight 0.two 0.8 four.53 interestingly, E. crassiminor1272 seems to choose circumneutral values whilst E. minor occurs 340 0 649 0 1272 4.29 7.69 10-5 at slightly acidic ones. E. crassiminor includes a larger weighted average -2.25 for sulphates whilst 2 0 six 2 0 3 two.69 10-2 E. minor has a higher optimum for manganese (Table 1). In unique, with reference to 0.6 0.two 0.two 9.eight 7.five 7.5 4.95 2.59 10-5 nitrogen, E. crassiminor seems to be associated with far more strict oligotrophy than E. minor. 101 0 40 37 0 107 -2.12 three.56 10-Figure three. (a). Box and whisker plots Haloxyfop Purity & Documentation displaying the ecological preferences of Eunotia crassiminor as when compared with E. minor. Figure 3. (a). Box and whisker plots showing the ecological preferences of Eunotia crassiminor as when compared with E. minor. Only environmental factors/parameters for which statistically substantial variations may very well be discovered are shown. Only environmental factors/parameters for which statistically considerable variations could be discovered are shown.Taxonomic comments.