Petroleum based hydrocarbon contamination includes petrol (gasoline), diesel type fuels, heavy fuel oils, jet fuels, bitumens, crude, hydraulic and lubricating oils. Similar compounds that are often classified as Petroleum Hydrocarbons come from pyrogenic processes such as Manufactured Gas Plants and include creosotes and tars. The proportion of aliphatic, aromatic and other chemicals that make up these compounds varies considerably between the types. To obtain accurate quantification, the calibrator used to create the calibration curve should be of the same type of hydrocarbon as found in the sample. This is true for laboratory methods as well as on site methods.
The problem for on site test kits and most on site analysers is that they cannot
identify the hydrocarbon in the sample. To calibrate these older systems, assumptions
have to be made about the hydrocarbon type in the sample, typically based on desk
study or initial SI data. Most test kits and analysers use a single compound, usually
diesel, for the TPH calibrator and a conversion factor can be applied to estimate
different hydrocarbon types. Unfortunately, for most hydrocarbon contaminated sites
the hydrocarbon in the sample analysed is rarely the same as the hydrocarbon identified
in the SI, or the hydrocarbon used to calibrate the analyser or test kit. This is
due to weathering and co-
Even the accredited laboratory analysers make an assumption about the type of hydrocarbon present, and for TPH analysis typically calibrate using diesel and lubricating oil. If the hydrocarbon in the sample is of a heavily weathered fuel, tarry or bituminous nature, the calibration will be incorrect and a new analysis should be run using a more appropriate calibrator.
The above QED fingerprint is from a fuel storage facility. The black line is the sample and the red line is the diesel calibrator fingerprint. It can easily be seen that if just a diesel calibrator had been used, a significant error in the calculated concentration would be made. The purple line is the amount of very degraded fuel remaining after the diesel has been subtracted.
The fingerprint above is from the same site as the sample to the left, but located a few metres away. The close match of the sample and the diesel calibrator fingerprint (red line) confirms diesel is the main hydrocarbon type, but that it is more degraded than the calibrator. QED can factor in the degradation to give a more accurate result.
The fingerprint above shows how QED can pull apart the black sample signal and identify the relative proportions that are comprised of degraded fuel (red line), diesel (blue line) and residual aromatics (purple line). The sample TPH is derived by calculating the concentration of each hydrocarbon type identified by applying the specific calibration curve for that hydrocarbon type and adding the results together. QED is calibrated with diesel, degraded fuel and PAH calibrators allowing each hydrocarbon type to be quantified using the most appropriate calibrator type.
The above fingerprint shows un-
The Advantage of Fingerprints for Hydrocarbon Identification
| Environment and Energy Award |
| Benefits of On Site analysis |
| Understanding Contaminated Land Analytical Testing |
| Uncertainty |
| Allotments & Gardens |
| Users |
| Pre-Aqusition of Land |
| Hydrocarbon Analysis |
| Heavy Metals Analysis |
| Chlorinated Solvents |
| Phenols |
| Ammonium |
| Cyanide |
| Other Contaminants |
| UVF Advantages |
| QED Fingerprinting |
| QED background subtraction |
| On Site quality control with QED |
| QED Correlation for TPH |
| TPH Analysis |
| QED correlation with PAH |
| ColorTec |