A managed riparian lowland in a glacial landscape (Holtum catchment, Denmark) was studied to quantify the relative importance of subsurface and surface flow to the recipient stream. The hydrogeological characterization combined geoelectrical methods, lithological logs, and piezometric heads with monthly flow measurements of springs, a ditch, and a drain, to determine seasonality and thereby infer flow paths. In addition, groundwater discharge through the streambed was estimated using temperature and water-stable isotopes as tracers. The lowland received large groundwater inputs with minimal seasonal variations from adjacent upland aquifers. This resulted in significant amounts of groundwater-fed surface flow to the stream, via man-made preferential flow paths comprising ditches, drainage systems, and a pond, and via two natural springs. Roughly, two thirds of the stream gain was due to surface flow to the stream, mainly via anthropogenic alterations. In contrast, direct groundwater discharge through the streambed accounted for only 4% of the stream flow gain, although bank seepage (not measured) to the straightened and deepened stream potentially accounted for an additional 17%. Comparison to analogous natural flow systems in the catchment substantiate the impact of anthropogenic alterations of riparian lowlands for the subsurface and surface flow components to their streams. through drains to the stream, or from groundwater-fed seeps (focused and/or diffusive) leading to overland flow, which is then routed to the stream.Hill [6] proposed different conceptual flow distribution models, where the hydrological controls were mainly determined by the size of the connected regional aquifer system and the thickness of the riparian aquifer. Several studies have since then, qualitatively confirmed these models. For example, studies [7,8] have demonstrated that flow across the lowland occurred as subsurface flow and groundwater-fed surface flow. Furthermore, Shabaga and Hill [8] demonstrated by dye tracer studies that surface flow took place as a combination of water discharging through macro-pores (soil pipes) and diffusively. Preferential flow through soil pipes in peat deposits has been shown to transmit large fluxes of water and with the possibility of causing springs resulting in overland flow [9].Measuring the individual flow paths is not a trivial task and thus not often done. Brüsch and Nilsson [10] attempted to measure total surface runoff (i.e., the sum of all overland flow) from a riparian zone and found an average surface runoff of 0.3 L s −1 , compared with stream flow of 24-38 L s −1 . Furthermore, diffuse discharge to the surface only accounted for 3% of the runoff, so most of this occurred through focused seeps. Shabaga and Hill [8] measured surface flow directly to a river at one site. Johansen et al. [11] measured flow in three springs and a network of ditches. In none of these studies, the direct seepage through the streambed was measured. It was therefore not possible to quantify the relative role of su...
Nutrients applied in connection with agriculture may enter the groundwater and ultimately end up in streams. Riparian lowlands have shown to hold the potential to significantly decrease nitrate (NO 3 ) concentrations in groundwater flowing from uplands to streams (
δ18O and electrical conductivity (EC) were used successfully to trace the spatial distribution of whole-lake groundwater-lake exchange for a small (four ha) groundwater-fed lake situated in a low relief and low hydraulic gradient area. The method relies on quick sampling of shallow groundwater, direct analysis of EC in the field, and relatively in-expensive analysis of δ18O in the laboratory. Ternary uncertain end-member mixing analysis (precipitation, groundwater, and lake water) quantified the composition of water discharging to and recharging from the lake. The tracer distribution and mixing analysis were in agreement with the interpreted groundwater flow near the lake. The use of only one tracer (either δ18O or EC) gave the same results for the recharge segments, but the discharge segments changed the origin of the water from being groundwater to precipitation controlled. The two tracers complemented each other, especially with different signals in precipitation and groundwater. The uncertain end-members were assessed based on local (groundwater and lake water) and off-site (precipitation) data. The off-site data were found to be useful if it contained representative information on local-site seasonality (uncertainty, variance). Final end-member concentrations could explain the transience of the hydrology at the site (i.e., flooding of the area adjacent to the lake during periods with high precipitation, and variability of the δ18O signal in precipitation). This methodology potentially represents a new option to study groundwater-lake systems. The tracer information collected over only two days is useful by itself for developing the next steps like the quantification of fluxes based on other standard methods (Darcy approach, seepage meters, or temperature). The tracer information can provide quantitative estimation of inputs and outputs by using the mixing analysis.
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