Groundwater storage as a major control of seasonal stream water quality dynamics during both base and storm flows
Abstract
Stream water quality exhibits dynamics at various time scales that are controlled by the spatiotemporal dynamics
of hydrobiogeochemical compartments, particularly by the dynamics of their connectivity to the stream. Based
on long-term catchment observations from the AgrHyS Observatory (France), we established relationships
between stream water quality and groundwater storage dynamics on various time scales. Those observations
combine stream water concentrations of Dissolved Organic Carbon (DOC), Nitrates (NO3) and Phosphorus (SRP)
concentrations, and a network of piezometers along 2 transects to characterize groundwater storage and quality in
space and time.
At the annual scale, the rise of groundwater table is delayed between the riparian area (early autumn) and
the upslope area (winter). This time lag along the hillslope is identified as the dominant control of the seasonal
signal in stream base flow nutrient concentrations.
-DOC and SRP are mobilized from organic upper soils layers when reached by the groundwater table. Firstly,
groundwater table rises in the riparian area, and connects the C and P sources in the organic rich riparian soils
leading to high stream DOC and SRP concentrations. Then, while groundwater connectivity remains high in
the riparian area, these sources are depleted leading to a progressive decrease in stream base flow DOC and
SRP concentration. In the recession and low flow periods, shallow groundwater contribution decreases and other
processes can influence stream concentrations.
-NO3 are mobilized from upslope shallow groundwater and therefore nitrate annual dynamics follows the annual
fluctuations of catchment water storage. At the start of the water year, the water table rise in the denitrified riparian
area leads to low stream nitrate concentrations. Then, the water table rise in the upslope area leads to sudden
increase in stream nitrate concentration. In the recession period, the nitrate concentration decreases variably
depending on the dynamics of the groundwater recession, itself controlled by climate and vegetation demand.
Groundwater dynamics appear to control concentration dynamics not only during base flow period but also
during storm events. Most of the storms occur during winter when groundwater is high and sub-surface connectivity
maximal. Conversely, the events that occur during dry periods can depict very different stream concentration
response because of reduced subsurface connectivity due to deeper groundwater table, leading to more variable
storm flowpaths.
The two studied hillslopes show contrasting groundwater nitrate concentrations, soil organic matter and
soil phosphorus content. These differences are mainly attributed to the difference in soils-groundwater interactions
and in past and current farming practices.
This conceptual model of the effect of spatio-temporal variations of groundwater table depth on soil and
stream water quality highlights the importance of shallow groundwater in controlling the non-stationarity and the
spatial variability of water quality response in catchments. This offer new constrains for modelling water quality
at different time scales.