Contamination of groundwater by pathogenic bacteria, protozoa, and viruses of fecal origin has been associated with waterborne disease outbreaks across various hydrogeological environments worldwide. Significantly, the extent of such microbiological contamination and transport of waterborne pathogens in aquifers is still not well understood (Bradford & Harvey, 2017;Cronin & Pedley, 2002). Generally, groundwater is considered to be less vulnerable than surface water to microbial pathogenic contamination from fecal matter, however, polluted groundwater is still responsible for a disproportionate fraction of reported waterborne disease outbreaks, particularly in developing countries and rural regions (Bradford & Harvey, 2017;Buckerfield et al., 2019;Jin & Flury, 2002; WHO & UNICEF, 2014). Furthermore, this problem is shared in developed countries such as the United States where between 750,000 and 6 million illnesses per year have been attributed to contaminated groundwater (Macler & Merkle, 2000;Reynolds et al., 2008). Serious cases of pathogenic bacterial contamination of aquifers have been reported following episodic heavy rain events, a notable example occurring at Walkerton (Ontario, Canada) in May 2000, where the rapid transport of pathogenic contaminants through a highly fractured carbonate aquifer system to water supply wells resulted in 2,300 illnesses and 7 deaths (O' Connor, 2002;Worthington & Smart, 2017). Many incidences of waterborne diseases can be associated with contamination of surface water and groundwater due to failing on-site domestic wastewater treatment systems (DWTSs), spreading of agricultural fecal matter (i.e., manure) and other farming activities in rural and less urbanized areas (Fetter, 2001;WHO, 2003). Despite a decrease in recent decades in waterborne disease outbreak risks related to municipal water supply sources, no corresponding decrease in disease outbreak risks for untreated or inadequately treated groundwater has been observed on the basis of outbreak reports (Craun, 2012). Hence, microbial pathogenic contamination of aquifers remains an ongoing, globally important, water quality problem (Ashbolt, 2004;Nguyen et al., 2016). Moreover, as a result of increasing numbers of point and nonpoint sources of fecal pollution in catchments (Barrett et al., 1999;Cronin & Pedley, 2002;Misstear et al., 1996), population growth, extreme weather events associated with climate change, and rapid land-use alterations, it should be expected that such water quality problems will be exacerbated in the