Worldwide, groundwater is one of the most important sources for fresh water supply. Approximately 70% of the Dutch population relies on groundwater for their drinking water, especially in the southern and eastern parts of the Netherlands where unconsolidated sandy deposits provide the best aquifers. Globally, groundwater resources are under pressure from overexploitation (Aeschbach-Hertig & Gleeson, 2012;Gleeson et al., 2012) and point and diffuse sources of pollution, especially by pesticides and nutrients from intensive use of agricultural lands. (Hansen et al., 2010;Nolan et al., 1997;Visser et al., 2007). The Netherlands is one of the most densely populated countries with an economy that is partly based on its agricultural sector. These two factors lead to high water demands and pressures on the groundwater system. The strong increase of intensive livestock farming in the Netherlands has created an increasing pressure on the groundwater pumped for drinking water supply (Mendizabal & Stuyfzand, 2011, Mendizabal et al., 2012. Although European legislation (EU, 2006) aims at reducing the leaching of agricultural contaminants to groundwater and surface water resources, many well fields for public water supply are still under threat. This resulted in the systematic closure of shallow well fields during the past 3 decades. Blending of water from different aquifers and different locations is often required to satisfy drinking water standards (e.g., Visser et al., 2013). Moreover, new developments put pressure on the available groundwater resources, such as the exponential increase of aquifer thermal energy systems in urbanized areas (Bonte et al., 2011) and the increased demands for irrigation from groundwater due to water scarcity during dry summers in agricultural areas.