The primary test study for monitoring contaminated land remediation using 4D ALERT technology was the Contaminated Land: Assessment of Remediation by Electrical Tomography (CL:ARET) project.
This was undertaken from November 2007 to January 2009, and was funded by a grant from the Technology Strategy Board (project TP/5/CON/6/I/H0048B) and contributions from a consortium partnership comprising VHE Construction PLC, the British Geological Survey, Interkonsult Ltd and South Kesteven District Council.
Traditional intrusive sampling can only test statistically small volumes of ground; therefore assessing the effectiveness of remediation techniques with certainty can be difficult and time-consuming.
But time-lapse geoelectrical imaging can act as a surrogate monitoring technology for tracking and visualising changes in contaminant concentrations, whether through natural processes or active remediation.
When combined with intrusive sampling calibration, it has the potential to produce easily visualised volumetric time-dependent (4D) maps of contaminant distributions.
The project test site was a municipal car-park on the site of a former gasworks in Stamford, Lincolnshire.
The site had been polluted by a range of polyaromatic hydrocarbons and dissolved phase contaminants. It was designated statutory contaminated land under Part IIA of the Environmental Protection Act due to the risk of polluting an underlying minor aquifer.
An ALERT system with a wireless communications link was installed on site, with 224 electrodes in 14 vertical boreholes drilled to depths of 8 m below ground level.
The arrays were arranged along two boundaries of the site, bordering a river and privately owned land. The aim of the installation was to monitor changes in groundwater quality following the completion of a remediation programme.
Monitoring took place for a period of just over one year, during which time no geoelectrical evidence of remnant pollution migration was detected.
The average resistivity of the minor aquifer exhibited a steady increase in resistivity for the first six months, after which it remained approximately constant.
In the absence of seasonal changes due to temperature or infiltration, it was concluded that the increase in resistivity was likely to be due to an improvement in the quality of groundwater, i.e. a decrease in dissolved contaminants.
A tracer test was undertaken to investigate the groundwater flow direction and speed, and to demonstrate the ability of ALERT to directly visualise natural attenuation processes (and by inference, other remediation processes).
A saline tracer was introduced into the minor aquifer, and its dilution and dispersal were mapped at high spatial and temporal resolutions (25 cm and 4 hours respectively).
The tracer test confirmed that no new pollution pathways were created during the installation of the borehole electrode arrays.
The directly observed dispersal of the tracer enabled the calculation of the groundwater seepage velocity, which was found to be in excellent agreement with estimated values.
Although natural attenuation processes were studied in this case, there is no reason why the concept should not be equally applicable to most other in-situ remediation techniques.
For further information download our Contaminated Land ALERT flyer or contact:
Dr Paul Wilkinson
British Geological Survey
Tel: +44 (0)115 936 3086
Email: Dr Paul Wilkinson
Dr Jonathan Chambers
Team Leader - Geophysical Tomography
Tel: +44 (0)115 936 3428
Email: Dr Jonathan Chambers