Abstract

The management of rivers for navigation, hydropower and flood risk reduction involves the installation of in-channel structures. These influence river levels and can affect groundwater flow within hydraulically-connected riparian floodplain aquifers. A comprehensively monitored, peri-urban, lowland river floodplain in the southern United Kingdom was used to explore these dependencies and to examine the implications for the flux exchange of water and nitrate between the river and the floodplain alluvial aquifer. The study demonstrated that rivers maintained at high levels by management structures, result in raised groundwater levels in the adjacent aquifer and complex groundwater flow patterns. Engineered river management structures were shown to promote flow from river to aquifer through the river bed but the majority of the associated nitrate was removed in the hyporheic zone. High-nitrate groundwater recharge to the alluvial aquifer also occurred through overbank flood flows. Across the floodplain, substantial denitrification occurred due to anaerobic conditions resulting from carbon-rich sediments and the shallow water table, the latter linked to the river management structures. An upper limit on the total annual mass of nitrate removed from river water entering the floodplain aquifer was estimated for the study site (2.9 × 104 kg), which was three orders of magnitude lower than the estimate of annual in-channel nitrate flux (1.8 × 107 kg). However, this capacity of lowland floodplains to reduce groundwater nitrate concentrations has local benefits, for example for private and public water supplies sourced from alluvial aquifers. The insights from the study also have relevance for those considering schemes that include the installation, removal or redesign of river management structures, as the resultant change in groundwater levels may have consequences for floodplain meadows and the nutrient status of the aquatic system.

Highlights

  • Floodplains are locations of complex interactions between river water, groundwater and overland flow (Burt et al, 2002)

  • Where permeable near surface floodplain sediments occur, Doble et al (2012) showed overbanking river water can result in substantial groundwater recharge

  • The Oxford floodplain setting has its own specific characteristics, it was used here to highlight general issues relating to the influence of managed rivers on groundwater flows within floodplain aquifers, and the implications for the flux of NO3−

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Summary

Introduction

Floodplains are locations of complex interactions between river water, groundwater and overland flow (Burt et al, 2002). The degree of interaction is dependent on a number of factors, including: the magnitude and direction of the head gradient between river and aquifer; the permeability of the alluvial sediments and the river bed material; and the capacity of the river channel to retain high flows (Sophocleous, 2002). Naganna et al (2017) provide a comprehensive review of the controls on river bed permeability identifying the importance of the particle size and depth of the bed material, the river channel geometry and upstream sediment supply to the river. Where permeable near surface floodplain sediments occur, Doble et al (2012) showed overbanking river water can result in substantial groundwater recharge

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