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271 - Field evaluation of nitrate transport and matrix storage<br />

processes in Prince Edward Island’s fractured sandstone aquifer<br />

Amanda Malenica, Steven Chapman, Beth Parker, & John Cherry<br />

G360 Centre for Applied Groundwater Research, University of Guelph, Ontario, Canada<br />

Mark Grimmett & Yefang Jiang<br />

Science and Technology Branch, Agriculture and Agri-Food Canada, Charlottetown, Prince<br />

Edward Island, Canada<br />

Cathy Ryan<br />

Department of Geoscience, University of Calgary, Calgary, Alberta, Canada<br />

The province of Prince Edward Island (PEI) is unique in Canada because 100% of the<br />

population is reliant on groundwater for drinking water supply. Of PEI’s total land area,<br />

42% is cleared for agricultural use, 15% of which was planted with potatoes in 2014 (PEI<br />

DAF, 2014). Nitrate concentrations have increased steadily in municipal and domestic<br />

wells and in surface water since the mid-1980s, as have the production of potatoes. Ecological<br />

impacts are detrimental to estuarine biota and evidenced by visible eutrophication<br />

and anoxic events. Although beneficial management practices (BMPs) have been identified<br />

and implemented, groundwater and surface water nitrate concentrations have not decreased<br />

substantially. The accumulation of nitrate mass diffusing into the porous rock matrix<br />

over time from fractures that dominate groundwater flow could be impeding the rate<br />

of nitrate concentration decrease. The relatively low-K rock matrix between the fractures<br />

constitutes the storage capacity of a dual-domain flow and transport system. Improvements<br />

in groundwater quality resulting from reduced nitrate loading are likely tempered<br />

by back-diffusion of the nitrate stored in the matrix where diffusion back to the fractures<br />

could delay down-gradient improvements in water quality.<br />

The objective of this study was to characterize the nitrate distribution at two different<br />

study sites within a discrete fractured network (DFN) context, including quantitation of<br />

nitrate concentrations in the rock matrix. Continuous cores, up to 45 m deep, were logged<br />

for lithology, discrete fractures and advective pathways. Discrete depth samples were collected<br />

adjacent to fractures and at varying distances into the matrix between fractures to<br />

quantify the immobile nitrate porewater concentrations and evaluate the magnitude of<br />

attenuation by diffusion and redox controlled reactions. Results showed local peaks in<br />

matrix nitrate concentrations, as high as 36 mg/L-N, primarily in the partially saturated<br />

overburden and upper saturated fractured bedrock. Nitrate concentrations did not completely<br />

attenuate with depth. This suggests the denitrification process is not strong, likely<br />

due to lack of electron donors and oxygenated conditions. Multi-level monitoring systems<br />

(MLS) were designed to facilitate high–resolution spatial and temporal measurements of<br />

mobile groundwater in fractures (hydraulic head, nitrate and other major ions and isotopes).<br />

Results demonstrate the influence of various mechanisms, including matrix diffusion<br />

and redox conditions, on the movement and attenuation of nitrate. Understanding<br />

these controlling processes is critical to informing conceptual models of flow and transport<br />

in sedimentary bedrock aquifers and understanding efficacy of BMP implementation and<br />

for development of sustainable agricultural practices.<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

147

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