A rock-glacier – pond system (NW Italian Alps): Soil and sediment properties, geochemistry, and trace-metal bioavailability
Introduction
Rock glaciers are slowly flowing mixtures of rock debris and ice, and constitute prominent sedimentary linkages within the alpine environment (Giardino et al., 1987). Rock glaciers act as efficient sediment conveyors in mountainous environments (Delaloye et al., 2010, Gärtner-Roer, 2012), transferring large quantities of debris from their rooting zone (upslope area) to their fronts (Kummert et al., 2018), and potentially impacting surface waters located downstream (Kummert and Delaloye, 2018a). Lakes and ponds can also form as a consequence of stream and river channel interruption due to rock-glacier advancing movement (Blöthe et al., 2019).
Melting ice in rock glaciers can impact the chemical characteristics of surface freshwater (Colombo et al., 2018a). Indeed, several studies report higher concentrations of trace metals and nutrients in their meltwaters in comparison to surface waters not affected by rock-glacier presence (Williams et al., 2006, Williams et al., 2007, Thies et al., 2013, Ilyashuk et al., 2014, Ilyashuk et al., 2018, Fegel et al., 2016, Colombo et al., 2018b, Colombo et al., 2019). Metals in rock-glacier-affected surface waters have been also shown to bioaccumulate, potentially impacting aquatic communities (Thies et al., 2013, Ilyashuk et al., 2014, Ilyashuk et al., 2018).
High-elevation impounded surface waters are key freshwater reference sites for global scale processes, due to minimal direct human influence and because of their rapid response to climate-related changes (Adrian et al., 2009, Salerno et al., 2014). Recent studies have demonstrated that lakes and ponds (defined as a water bodies < 2 × 104 m2, Hamerlík et al., 2014) affected by rock-glacier ice melting have suffered changes in their chemical and biological status (Ilyashuk et al., 2014, Ilyashuk et al., 2018), especially in the context of climate change during the last decades (Thies et al., 2007). Recent climatic changes have caused strong modifications in glacial and permafrost environments at global scale (Harris et al., 2009, Zemp et al., 2015, Biskaborn et al., 2019) and, specifically, in the NW Italian Alps (Giaccone et al., 2015, Colombo et al., 2016a, Colombo et al., 2016b).
Although a growing literature has documented the role of rock-glacier ice melting in impacting the alpine headwater hydrochemistry, there is a paucity of studies that investigated the influence of rock glaciers on sedimentological, hydrochemical, and ecological dynamics of surface waters located downstream. In this context, the Col d’Olen area (NW Italian Alps) represents a suitable model system. In fact, in this area, an intact rock glacier terminates into a pond and solute-enriched waters originating from the rock glacier flow into the pond through a subsurface hydrological window (Colombo et al., 2018b, Colombo et al., 2018c).
Our hypothesis is that the rock-glacier dynamics may influence the pond in terms of lacustrine sediment geochemistry and bioavailability of trace metals for aquatic organisms, potentially exerting adverse effects. In order to test this hypothesis, we sampled both soils and sediments in different compartments of the rock-glacier - pond system and we further sampled benthic invertebrates in the pond to: (i) assess the potential influence of the rock glacier and the surrounding soils on the lacustrine sediment geochemistry, (ii) investigate trace-metal bioaccumulation in aquatic organisms, and (iii) attempt to assess the effect of rock-glacier dynamics on potential pond systemic modifications.
Section snippets
Study area
The research site is a node of the Long-Term Ecological Research (LTER) network (Angelo Mosso Scientific Institute site) in Italy, in the North-Western Italian Alps, at the boundary between Valle d’Aosta and Piemonte regions (Fig. 1a). The Col d’Olen Rock Glacier Pond is situated at an elevation of 2722 m a.s.l. and its catchment area is approximately 206,000 m2 (Fig. 1b).
The Col d’Olen Rock Glacier can be classified as an intact bouldery, talus-tongue shaped rock glacier (cf., Haeberli et al.,
Thermal regime of the ground surface and ice content in the rock glacier
The thermal regimes of the ground surface show that MAGST (2.5 °C), GFI (–6 °C·day), and WEqT (0.1 °C) in the soil are far higher than on the rock glacier (Table 1), with values clearly indicating permafrost absence (Colombo et al., 2019). MAGST close to 0 °C, and decidedly negative GFI and WEqT confirm conditions favouring permafrost existence in the rock glacier, showing the well-known “negative thermal anomaly” characterising this coarse deposit (c.f., Harris and Pedersen, 1998), especially
Discussion
Despite the increasing interest on the effects of rock-glacier ice melting, a lack of knowledge exists about the influence of rock-glacier sediment transfer and hydrochemical dynamics on the geochemical and ecological characteristics of a connected hydrological system. By analysing the physiochemical, geochemical, and ecological conditions of the rock glacier and of the surrounding lacustrine and terrestrial soil, we attempt to highlight the main differences and the possible connections among
Conclusion
In this study we show that the unique characteristics of the rock-glacier environment (i.e., cold ground thermal regimes, ground-ice presence, and coarse debris cover) and its lithology (serpentinites) influence the rock-glacier geochemistry and ecology in comparison to surrounding areas. Fine-grained sediment transfer from the rock glacier to the pond is probably the most important process affecting the geochemistry of lacustrine sediments. It is likely that the rock-glacier advance has
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
We would like to thank Gaetano Viviano, Cristina Viani, Marco Bacenetti, Gioachino Roberti, Ilaria Mania, Roberta Gorra and Elena Serra for their help in field work activities. We are also grateful for the support given by Daniele Bormioli, Giuseppina Moletta and Giacomo Re Fiorentin (Arpa Piemonte), and Marco Giardino, Luigi Perotti, Lino Judica and Adriana Bovio (University of Turin). We give special thanks to the family Beck-Peccoz, Consorzio di Miglioramento Fondiario di Gressoney (Aosta)
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