Analysis of aquifer heterogeneity within a well capture zone, comparison of model data with field experiments: A case study from the river Wiese, Switzerland

Abstract

This paper describes two groundwater models simulating a well capture zone in a heterogeneous aquifer located near an infiltrating river. A deterministic, largescaled groundwater model (1.8 ¥ 1.2 km) is used to simulate the average behavior of groundwater flow and advective transport. It is also used to assign the boundary conditions for a small-scaled groundwater model (550 ¥ 400 m) which relies on stochastically generated aquifer properties based on site-specific drill core and georadar data. The small-scaled groundwater model is used to include the large subsurface heterogeneity at the location of interest. The stochastic approach in the small-scaled groundwater model does not lead to a clearly defined well capture zone, but to a plane representation of the probability of a certain surface location belonging to the well capture zone. The models were applied to a study site, which is located in an area of artificial groundwater recharge and production, in Lange Erlen near Basel, Northwestern Switzerland. The groundwater at this site contributes to the city's drinking water supply, and the site serves as a recreational area to the population of Basel. The river is channelized, but there are initiatives to restore the riverbank to more natural conditions. However, they conflict with the requirements of groundwater protection, especially during flood events. Therefore, a river section of 600 m in the vicinity of an unused and disconnected drinking water well was restored to study changes in the Aquatic Sciences groundwater flow regime depending on hydrologic variations, water supply operation data, progress of river restoration, and subsurface heterogeneity. The results of the groundwater models are compared with data from two tracer experiments using Uranine and the natural Radon isotope Rn-222, and with physical, chemical, and microbiological data sampled in monitoring wells between the river and the drinking water well. The groundwater models document significant variations regarding the dimension of the well capture zone depending on changing boundary conditions and the variability of the hydraulic aquifer properties. The knowledge of the subsurface heterogeneity is important to evaluate transport times and distances of microorganisms from the infiltrating river or the riverbank to the drinking water well. The data from the monitoring wells show that chemical and microbiological processes predominantly occur in the hyporheic interstitial zone and the riverbank within a range of a few meters up to a few 10s of meters from the river. The methods presented here can be used to define and evaluate groundwater protection zones in heterogeneous aquifers associated with infiltration from rivers under changing boundary conditions, and under the uncertainty of subsurface heterogeneity. Furthermore, they allow one to study the sitespecific operational alternatives associated with river restoration.

A Sedimentological Model to Characterize Braided River Deposits for Hydrogeological Applications

“…Files containing distributions of hydraulic conductivity and effective porosity values were generated and exported to a Modflow-based groundwater simulation system, in order to perform groundwater flow and transport simulations (PMWIN, Chiang & Kinzelbach, 2001). This process is described in detail in Regli et al (2003). Groundwater flow and transport simulations are in accordance with field measurements including tracer breakthrough concentrations and groundwater head measurements.…”

Towards improved instrumentation for assessing river-groundwater interactions in a restored river corridor

“…Each restoration project is potentially an opportunity to learn more about aquatic systems and how they are modified following restoration (Kondolf, 1998;Regli et al, 2003). Adequate process knowledge is fundamental to understanding the impact of river restoration on groundwater systems.…”

“…Details of individual techniques have already been published by ), Diem et al (2010, Doetsch et al (2010a,b;, Schäppi et al (2010), and Vogt et al (2009;2010a,b). The special issue, in which this paper appears, contains additional descriptions about individual aspects (Edmaier et al, 2011;Hoehn and Scholtis, 2011;Linde et al, 2011;Pasquale et al, 2011;Samaritani et al, 2011). In this paper, we put these individual contributions into a common context.…”

Multivariate Analysis of Groundwater-Quality Time-Series Using Self-organizing Maps and Sammon’s Mapping

“…Not all conditions enable the filter capacity to remove river-borne microbial contamination before it reaches groundwater extraction wells (Taylor et al 2004;Dash et al 2010). Increased infiltration of river water into an aquifer during high discharge events can result in microbial contamination of drinking water extraction wells (Regli et al 2003). The contamination potential is strongly dependent on the nature of high discharge events, the location of the extraction wells relative to the river and the composition of the aquifer material and river bed (Regli et al 2003;Page et al 2012).…”

“…Increased infiltration of river water into an aquifer during high discharge events can result in microbial contamination of drinking water extraction wells (Regli et al 2003). The contamination potential is strongly dependent on the nature of high discharge events, the location of the extraction wells relative to the river and the composition of the aquifer material and river bed (Regli et al 2003;Page et al 2012). Alongside these spatial considerations, the duration and level of contamination, the filter capacity and the distance travelled by the freshly infiltrated water are influenced by temporal factors including (a) the history of high discharge events, (b) the relative change in river stage over time, (c) seasonality, (d) the varying load of river water contaminants (Regli et al 2003).…”