Environmental gradient relative to oxbow lake-meandering river connectivity in Zoige Basin of the Tibetan Plateau
Introduction
Floodplains are an important alluvial complex of a widely inter-connected series of biotopes and ecological gradients that, with their unique landscapes and biotic communities, create riverine wetland ecosystems. Floodplain lakes are a common component of riverscape. Together with terrestrial landscape they generate a mosaic floodplain of specific environmental gradient (Ward, 1998), resulting in highly diverse aquatic habitats, communities, and ecological processes within river corridors (Arscott et al., 2005; Marshall et al., 2006).
Within meander belts of meandering rivers, oxbow lakes are one of the most typical geomorphic units that generated from neck or chute cutoff through lateral bank erosion and overbank flooding (Leopold and Wolman, 1957; Crosato, 2008; Durkin et al., 2015). These lakes are abandoned channels of meander bends and are physically isolated from original channels, usually with U- and Ω-shaped water bodies (Knight et al., 2002; Delhomme et al., 2013). As oxbow lakes age, due to flooding input and sediment deposition, they become shallower, smaller, and gradually disconnected from the active meandering channel (Winemiller et al., 2000; Miranda, 2005). Based on hydrological connectivity of oxbow lakes and meandering rivers, researchers usually divide oxbow lakes into three types: (i) lotic lakes that permanently connect with the active channel at both ends, (ii) semi-lotic lakes that connect at only downstream ends, and (iii) lentic lakes that temporarily connect during high flows (e.g., Obolewski, 2013; Kobus et al., 2016).
Because of this spatial heterogeneity, within a meander belt, existing lakes that at a wide range of aging phases can show large between-lake variation in terms of geometry, trophic state, and aquatic vegetation (Amoros and Bornette, 2002; Miranda, 2005), thereby providing diverse habitats that facilitate biodiversity (Acreman et al., 2007; Obolewski, 2011), as well as offering different socio-economic benefits in terms of fishery, recreation, and flood mitigation. Researchers have done many field surveys concerning oxbow lake ecosystems, and we sum them up in two main aspects.
First, the patterns of association between hydrological connectivity and lake chemical variables, and assemblages of fish, macroinvertebrate, and zooplankton. Previous studies have examined the correlations among aquatic life (e.g., abundance, structure, and diversity), aquatic physical-chemical properties (e.g., pH, dissolved oxygen (DO), turbidity, and dissolved nutrients), and connectivity reflected by lake geometry (e.g., area, depth, and distance from active channel), and have revealed several predictable patterns (e.g., Glinska-Lewczuk, 2005; Gallardo et al., 2008; Kufel and Leśniczuk, 2014; Kobus et al., 2016). For example, Winemiller et al. (2000) found that concentration of dissolved nutrient was the best predictor of fish species diversity, and the negative correlation between dissolved nitrogen and species diversity implied that nutrient-rich oxbow lakes were severe habitats in which many species would not survive.
Second, the evaluation of oxbow lakes restoration projects. The effectiveness of oxbow lakes reconnection has been widely assessed based on the comparison between before and after of these projects, in terms of mainly biodiversity and water quality (e.g., Gallardo et al., 2012; Seidel et al., 2017). Most of the assessments have suggested that the reconnection of oxbow lakes to active meandering channels was of great potential to improve aquatic ecosystem.
Previous studies have certainly extended the knowledge of biogeochemical processes within oxbow lakes, however there are still knowledge gaps. First, the focus mainly has been on organisms. Although nutrients are essential for survival, growth, and recruitment of aquatic species, their associations with lake-channel connectivity and related lake geometry have received relatively less attention. Second, lacking focus of oxbow lakes in highland floodplains (>3000 m), whilst alpine climate may influence the relationship between connectivity and environmental variables. For example, in contrast to the intermediate disturbance hypothesis that suggests the highest biodiversity occurs in lakes with intermediate connectivity, i.e., a unimodal response (Connell, 1978; Ward et al., 1999; Amoros and Bornette, 2001), Zhou et al. (2019) observed that reduced connectivity could benefit macroinvertebrate assemblages in oxbow lakes in the Tibetan Plateau. Therefore, previous lake restoration measures may not be applicable for alpine oxbow lakes. Moreover, within previous studied meander belts, researchers usually chose less than ten oxbow lakes to monitor, thus might not able to represent the broad range of lake-channel connectivity.
To address these questions, we chose an oxbow lake group along a high-sinuosity tributary of White River, a typical meandering river located at Zoige Basin, the northeastern Tibetan Plateau, to conduct field measurement and sampling at the beginning (May) and the end (September) of the flood season in 2019. We selected 24 lakes and recorded their geometry and connectivity, and measured physical-chemical properties of lake water and river water. We aimed to test the hypothesis that predictable patterns in water properties arise relative to lake geometry and connectivity. This work will help to establish principles towards restoring alpine oxbow lakes ecosystem.
Section snippets
Site description
The oxbow lakes this work studied belong to a meander belt (~1000 m in width) of a tributary of White River, a meandering river located at Zoige Basin, the northeastern Tibetan Plateau, that suffers from frequent neck cutoffs (Li and Gao, 2019a, Fig. 1). High altitude (>3500 m) subjects White River catchment (5488 km2) to cold and windy alpine climate, with mean annual air temperature 0.7–1.1 °C, and mean annual precipitation 649 mm, mostly concentrated in the flood season (May to September).
Lake geometry
Mean width of the studied oxbow lakes was ~17 m, and no significant differences in lake width were found among all types of lakes (Fig. 3(c)). Lake length however significantly decreased from lotic (441 m) to semi-lotic lakes (384 m) and eventually to lentic lakes (213 m, Fig. 3(b)). Lake area and length/width ratio obeyed the order of length, i.e., significantly decreased from the most connected lakes to the most disconnected lakes (Fig. 3(a) and (d)). Lentic, semi-lotic, and lotic lakes had
Environmental gradient relative to lake-channel connectivity
At the beginning of the flood season water level just started to increase, samples in May thus could represent water properties and the production, transportation, and accumulation of nutrients in the last non-flood season during which lake-channel connectivity remained constant. Fig. 4, Fig. 5 and Table 3 demonstrated the significant differences in water properties across the meander belt. Oxbow lakes differed not only from the channel, but also among their different types. Except for pH,
Conclusion
Oxbow lakes generated from meander cutoffs are an important component of aquatic habitat and lake-channel ecosystem. We studied water properties of oxbow lakes in a meandering river developed in an alpine peatland in Zoige Basin of the Tibetan Plateau. Within the meander belt, we found an environmental gradient associated with lake-channel connectivity. Lentic lakes and semi-lotic lakes tended to have higher dissolved oxygen and nutrients concentrations in comparison with lotic lakes and the
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.
Acknowledgements
This study was supported by the National Natural Science Foundation of China (51979012, 51979120, 51709020, 31600378), Open Research Fund Program of State key Laboratory of Hydroscience and Engineering (sklhse-2019-A-03), and Scientific Research Fund of Hunan Provincial Education Department (19A017), and Natural Science Foundation of Hunan Province, China (2020JJ3036). We thank Tao Tang, Hanyou Lu, Yilun Liu, Bang Chen, and Jingwen Bai for field assistance and laboratory works, and thank Yize
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