Publication | Open Access
Field performance of the radon-deficit technique to detect and delineate a complex DNAPL accumulation in a multi-layer soil profile
16
Citations
45
References
2020
Year
The performance of the radon (<sup>222</sup>Rn)-deficit technique has been evaluated at a site in which a complex DNAPL mixture (mostly hexachlorocyclohexanes and chlorobenzenes) has contaminated all four layers (from top to bottom: anthropic backfill, silt, gravel and marl) of the soil profile. Soil gas samples were collected at two depths (0.8 m and 1.7 m) in seven field campaigns and a total of 186 <sup>222</sup>Rn measurements were performed with a pulse ionization detector. A statistical assessment of the influence of field parameters on the results revealed that sampling depth and atmospheric pressure did not significantly affect the measurements, while the location of the sampling point and ground-level atmospheric temperature did. In order to remove the bias introduced by varying field temperatures and hence to be able to jointly interpret <sup>222</sup>Rn measurements from different campaigns, <sup>222</sup>Rn concentrations were rescaled by dividing each individual datum by the mean <sup>222</sup>Rn concentration of its corresponding field campaign. Rescaled <sup>222</sup>Rn maps showed a high spatial correlation between <sup>222</sup>Rn minima and maximum contaminant concentrations in the top two layers of the soil profile, successfully delineating the surface trace of DNAPL accumulation in the anthropic backfill and silt layers. However, no correlation could be established between <sup>222</sup>Rn concentrations in superficial soil gas and contaminant concentration in the deeper two layers of the soil profile. These results indicate that the <sup>222</sup>Rn-deficit technique is unable to describe the vertical variation of contamination processes with depth but can be an effective tool for the preliminary characterization of sites in which the distance between the inlet point of the sampling probe and the contaminant accumulation falls within the effective diffusion length of <sup>222</sup>Rn in the affected soil profile.
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