4 Applied Research at Northeastern State Geological Surveys
Sunday, 20 March 2022
8:00 AM - 12:00 PM
Commonwealth Salon 1
DETERMINING THE INFLUENCE OF GROUNDWATER AND GROUNDWATER- SURFACE WATER INTERACTION ON PHOSPHOROUS LEVELS AND CYANOBACTERIA BLOOMS IN A SMALL EUTROPHIC LAKE USING A “CONTACT TRACING” APPROACH: NORTHERN VERMONT
Paper number: 4-4
Program: Theme Sessions
Time: 9:00 AM – 9:20 AM
Authors
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Peter RyanMiddlebury College, Middlebury, VT
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Max MemegerMiddlebury College, Middlebury, VT
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Julia BoylesVermont Geological Survey, Montpelier, VT
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Grahame BradleyWaste Management and Prevention Division, Montpelier, VT
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Edwin RomanowiczSUNY Plattsburgh, Plattsburgh, NY
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Anna LoewaldMiddlebury College, Middlebury, VT
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Patti CaseyMontpelier, VT
Abstract
Our methodology is to first build a 3D framework for the lake basin in GIS from surficial and bedrock mapping, and the spatial analysis of private well logs (isopach, bedrock surface contour, and static water level (SWL) maps), and then to integrate the chemical analyses of groundwater and surface water samples into this framework. Nine shallow (<6 m) monitoring wells were completed around the lake perimeter to access the surficial aquifer. P loading to Lake Carmi can be derived from external (agriculture, shoreline development, and geogenic (bedrock and surficial materials)) and internal (lake sediments) sources. To discriminate between the external sources, we used a “contact tracing” approach where we examine specific chemical tracers that may accompany P in groundwater and surface water in each sample. Tracers useful for anthropogenic activity include NOX, NaCl, and herbicides, whereas geogenic tracers comprise major and trace elements derived from bedrock formations and surficial deposits. Stable isotope (2H and 18O) analysis of all water samples and recharge-ages of selected groundwater samples were also completed.
Preliminary results show that: 1) significant amounts of P are available in the vadose and saturated zone sediments for mobilization in groundwater; 2) By comparing monitoring well SWLs with lake level elevations, regions of inflow and outflow can be defined; 3) Trace element analysis of surface- and groundwater suggests a geogenic P source for some of the mobile P in groundwater; 4) Currently available P (total) data ranges are: 6-46 ppb for private water wells and springs, 18-418 ppb for monitoring wells, 60-127 ppb for tributaries, and 31-78 ppb for lake samples.
Geological Society of America Abstracts with Programs. Vol. 54, No. 3
doi: 10.1130/abs/2022NE-375321
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