GSA 2020 Connects Online

Paper No. 148-3
Presentation Time: 1:55 PM

ISOTOPIC ANALYSIS OF RADIONUCLIDE PRESENCE AT DISCRETE INTERVALS IN THE MIDWESTERN CAMBRIAN-ORDOVICIAN AQUIFER SYSTEM


MATHEWS, Madeleine1, SCOTT, Sean2, GOTKOWITZ, Madeline3 and GINDER-VOGEL, Matthew1, (1)Civil and Environmental Engineering, University of Wisconsin - Madison, 660 N Park St, Madison, WI 53706, (2)Wisconsin State Lab of Hygiene, 2601 Agriculture Dr., Madison, WI 53718, (3)Montana Bureau of Mines and Geology, Montana Tech, 1300 West Park Street, Butte, MT 59701

Naturally occurring contaminants like radium (Ra) pose a danger to groundwater as a drinking water source. The Midwestern Cambrian-Ordovician aquifer system (MCOAS), a source of drinking water for many municipalities in the Upper Midwest of the USA, is frequently observed to contain combined Ra (226Ra + 228Ra) above the maximum contaminant level of 5 pCi/L. Here, we investigate 226Ra associations with aquifer solids through a sequential extraction and digestion experiment, using sensitive multi-collector inductively coupled plasma mass spectrometry analysis to quantify the ultra trace Ra levels. We also compare parent 238U and daughter 226Ra isotope activities to determine Ra leachability. Equilibrium between parent and daughter isotope activities varies across stratigraphy, suggesting that Ra mobilization depends on minerals present in the bedrock layer in addition to the influence of local geochemical conditions releasing Ra to the aqueous system. The association between Ra and the aquifer solids varies across stratigraphy. Aquifer geochemical conditions will impact the release of Ra to the aqueous system differently in different stratigraphic units. Due to the heterogeneous nature of the aquifer system, the variation of stratigraphy presence across the extent of the aquifer suggests that Ra mobility varies due to local geochemical conditions and available mineral associations. This suggests that changes in groundwater flow from one part of the aquifer system to another may impact local geochemistry and mobilize naturally occurring contaminants.