This manuscript is contextually identical with the following published paper:
26During the transition from average to low water levels, the sediment shifted from severely anoxic to poorly 27 oxidised levels, with more favourable nutrient content while the amount of ammonia and sulphides decreased, too.
28It was shown that lowering water levels could act on plants via increased redox potential of the sediment and could 29 counteract the die-back of Phragmites, suggesting the effectiveness of water level decrease as a management 30 practice to counter reed die-back.
31Keywords: redox potential, morphology, growth dynamics, carbohydrates, water level changes 32 2
Introduction
33Water depth is one of the crucial factors that controls zonation, distribution and progression of Phragmites 34 australis within lakes (Coops et al., 1996; Vretare et al., 2001;Engloner & Papp, 2006;Tóth & Szabó, 2012).
35Numerous studies have shown that, due to specific cytological and biophysical features, common reed is able to 36 tolerate high and prolonged inundation (Armstrong et al., 1994; Crawford & Braendle, 1996; Vartapetian & 37 Jackson, 1997). A continuous gas space within the plant tissue called aerenchyma runs down from the aerial to the 38 underground parts of the plant, channelling air from leaves to rhizomes and roots. This flux of atmospheric gases 39 is driven by humidity-induced partial pressure differences between the air and the substomatal space (Armstrong & Armstrong, 1991). Without it, the reed could suffer complete or partial oxygen deprivation due to high microbial 41 oxygen consumption within the sediment (Brinson et al., 1981; Crawford & Braendle, 1996). To survive anoxic 42 conditions of the sediment the air from the aerenchyma is pressurised into the sediment surrounding reed roots via 43 radial diffusion creating an oxygenated rhizosphere (Armstrong et al., 1991; Beckett et al., 2001). This mechanism 44 cannot however compensate for effects of a severe or prolonged anoxia, which causes the temporary or permanent 45 die-back of plants.
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46Reed die-back in Europe is a thoroughly discussed topic and several causes have been proposed (Den Hartog 47 et al., 1989;Ostendorp, 1989; Crawford & Braendle, 1996;Fürtig et al., 1996;Kubín & Melzer, 1996;Brix, 1999; 48 Armstrong & Armstrong, 2001). The simultaneous and general nature of this phenomenon (many sites) indicates 49 that it could be caused by a widespread disturbance. In Lake Balaton, the process started in the 1970s (Kovács et 50 al., 1989; Virág, 1997). The die-back was similar in many cases: the stands lost their homogeneity and the 51 clumping of reed progressed with time, eventually leading to bands of clustered Phragmites at the affected sites.
52This phenomenon occurred predominantly at the maximal depth of reed penetration (i.e., at the lakeward side of 53 the stands), suggesting the importance of water depth and thus the water level fluctuation. In all cases, plant density 54 gradually decreased outside the clumps and eventually discret...