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Total Dissolved Gas Pressure Measurements for Assessing Contaminant Degradation Processes in Groundwater
Author(s) -
Roy James W.,
McLeod Heather C.,
Suchy Martin,
Smith James E.
Publication year - 2017
Publication title -
groundwater monitoring and remediation
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.677
H-Index - 47
eISSN - 1745-6592
pISSN - 1069-3629
DOI - 10.1111/gwmr.12194
Subject(s) - environmental chemistry , methanogenesis , environmental science , aquifer , groundwater , denitrification , hydrostatic pressure , degradation (telecommunications) , anoxic waters , water table , nitrate , chemistry , environmental engineering , methane , geology , nitrogen , telecommunications , physics , geotechnical engineering , organic chemistry , computer science , thermodynamics
The total dissolved gas pressure ( P TDG ) probe has been used in groundwater studies for over a decade, but rarely in assessing contaminant degradation, despite the many degradation reactions that produce or consume dissolved gases. Here we present three studies to demonstrate the application of P TDG measurements to groundwater experiencing contaminant degradation, with discussion of its benefits and limitations. The first study is a pilot‐scale laboratory experiment simulating dissolved ethanol contamination of an anaerobic sand aquifer. Continuous monitoring of P TDG showed the rapid onset of microbial hydrocarbon degradation via denitrification and fermentation. The subsequent formation of a gas phase was revealed when P TDG began mimicking the bubbling pressure ( P G *; sum of hydrostatic and atmospheric pressure), fluctuating with atmospheric pressure. Some deviations of P TDG above P G * occurred also, which may hold promise for signalling substantial changes in the rate or type of degradation process (here, the onset of methanogenesis). In the second study, synoptic field measurements at a petroleum plume site demonstrated how elevated P TDG could identify wells with evidence of hydrocarbon degradation (denitrification and/or methanogenesis). And finally, combined field measurements of dissolved oxygen (DO) and P TDG in monitoring wells of a nitrate‐contaminated aquifer (Abbottsford‐Sumas) revealed areas where denitrification was likely occurring. Limitations to P TDG use identified in these studies included the masking of degradation processes by the presence of a gas phase, as when trapped following water table fluctuations or formed from rigorous degradation reactions, and confounded assessment of P TDG patterns from other natural or anthropogenic processes that can also influence groundwater P TDG .