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aquifers and (ii) the uncertain integrity of domestic and farm wells, there is clearly a burden<br />

of proof on those sampling such wells to demonstrate that the ‘pre-drill’ data collected are<br />

robust and provide reliable information for use in dispute resolution and resource management.<br />

If the only purpose of such ‘baseline’ sampling is the collection of natural gas samples,<br />

then (i) the transient nature of natural gas emissions from oil and gas wells needs to be<br />

considered in terms of monitoring and (ii) sample collection must be optimized to reduce<br />

degassing at the well. Neither constraint is easily overcome with domestic wells.<br />

An exemplary protocol for testing of domestic and farm wells is that developed by Alberta<br />

Environment (Standard for Baseline Water Well Testing for Coalbed Methane/Natural<br />

Gas in Coal Operations, April 2006) that encourages (but does not require) the removal<br />

of the sanitary seal of a landowner’s well in order to conduct both a water-supply ‘yield<br />

test’ and GWQ sampling downhole. The additional expense (~$3,000 per well) of such a<br />

precaution may be considered as part of the cost of acquiring better scientific data from a<br />

water well not designed to yield scientifically reliable GWQ data.<br />

145 - Case Study Source Discrimination of a Benzene Release<br />

Using a Two-Dimensional (2D) Compound Specific Isotopic<br />

Analysis (CSIA) Approach<br />

Natalie Szponar, Brad J. MacLean, Tom H. Grimminck, Heather Stuart, & Rob F. Kell<br />

Dillon Consulting Limited, Oakville, Ontario, Canada<br />

In recent years, Compound Specific Isotope Analysis (CSIA) has emerged as an important<br />

tool in environmental forensics in assessing source(s) at contaminated sites, understanding<br />

comingled plumes and evaluating contaminant attenuation. This case study presents<br />

a Two-Dimensional (2D) CSIA approach that was used to gain a better understanding<br />

of the potential source(s) and age of benzene impacts to groundwater where no definitive<br />

source or release date had been identified.<br />

Extensive groundwater and soil characterization at the site of the case study identified benzene<br />

impacts in soil from 1 to greater than 4 meter below ground surface, with a maximum<br />

identified benzene concentration of 1,500 ug/g in soil; and 939,000 ug/L in groundwater.<br />

Although the characterization has provided a good understanding of the distribution of<br />

the benzene impacts, the source of the identified impacts and the time of release(s) were<br />

unknown. These unknowns were further complicated by the presence of numerous potential<br />

sources and a complex array of underground services and pipelines.<br />

Stable isotope techniques provide a powerful tool for source discrimination. In particular, stable<br />

carbon (δ 13 C) and hydrogen (δ 2 H) isotopes when plotted against each other for a specific<br />

compound (i.e., benzene) [referred to 2D-CSIA] can provide a “fingerprint” plot. This plot<br />

can be used to distinguish between different physical and biological processes affecting the<br />

compound, and may also provide further differentiation between different sources of refined/<br />

manufactured benzene product (based on source material and manufacturing process).<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

155

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