Resources
Part of the Oxford Instruments Group
Expand
Collapse
Part of the Oxford Instruments Group
Application Notes
Published: 01 Apr 2019 · Last updated: 03 Aug 2026
Fat, Oil and Grease (FOG) is often described as a pollutant since it is discharged in wastewater causing build-up and subsequent blockage of sewers. Therefore, it is a crucial parameter in environmental monitoring performed by water suppliers' laboratories and environmental authorities.
In the United States, "oil and grease" is classed as a conventional pollutant under the US Clean Water Act. The US Environmental Protection Agency method 1664 (solvent extraction followed by gravimetry) is used for survey and monitoring programs related to this and other legislation.
In the United Kingdom, the most commonly used method separates FOG from the water by passing it through a glass fibre filter (1.2 μm pore size). The FOG is extracted from the filter using petroleum ether (leaving the solid particulates behind) with the total amount determined by gravimetry after the solvent has been boiled off.
In contrast to the labour-intensive and destructive solvent extraction method, this application note describes a fast, accurate and solvent-free variant of the method whereby the FOG is directly measured on the filter without extraction.
Solvent extraction is commonly used for the measurement of FOG deposited on a filter. However, this method can be time consuming, requires skilled operators and the use of hazardous solvents.
In contrast:
The MQC+ benchtop NMR analyser provides an alternative to extensive wet-chemistry methods. FOG analysis with the MQC+ is quick and easy to perform, simple to calibrate and requires minimal sample preparation. As such it is ideal for non-specialist laboratory personnel and the whole process can be automated using the MQ-Auto autosampler.
Benchtop NMR detects the signal from oil and fat on a single filter sheet after the initial NMR signals from the solids and any residual moisture have decayed completely. The remaining signal intensity correlates with the mass of FOG on the sample.
Since NMR calibrations are always linear, only two well characterised standards are required to calibrate the analyser. However, it is recommended that the instrument is calibrated using at least 6 standard samples with known FOG contents, evenly distributed over the range of interest. The samples must be dry prior to the NMR measurement.
In this study, the calibration standards were prepared by adding 100 mg of the desired composition of fat, oil or grease (edible oil, animal fat, mineral oil, engine lubricant, etc.) to petroleum ether (100 ml), followed by adding aliquots of this mixture to clean filter sheets. After drying, the reference grease content of each standard was measured using a precision analytical balance to at least four decimal places (± 0.1 mg).
To prepare a sample for analysis, a dried filter sheet containing filtration residuals was folded and placed into a small glass vial. The samples were then temperature conditioned at 40°C in a dry block for a minimum of 20 minutes prior to measurement by the MQC+. The total measurement time for one sample was 5 minutes, excluding sample conditioning time.
Figure 1 shows a calibration obtained by measuring a set of calibration standards created by adding known amounts of a FOG mixture to various filter papers.
Fig. 1 — NMR calibration generated for the set of standards prepared using gravimetric data for the oil/fat mixtures. The correlation coefficient and standard deviation are 1.00 and 0.70 mg respectively.
A comparison of FOG content measurements performed on the calibration standards against gravimetry is shown in Table 1; it clearly shows that the NMR method is more accurate than solvent extraction (using petroleum ether).
Table 1. Comparison of solvent extraction and NMR results for FOG content against gravimetry
| Sample ID | Reference FOG content measured gravimetrically m0, mg | FOG content determined by extraction method m1, mg | FOG content measured by NMR method m2, mg | Difference |m0-m1|, mg | Difference |m0-m2|, mg |
| 1 | 0.6 | 0.3 | 0.9 | 0.3 | 0.3 |
| 2 | 0.8 | 0.6 | 0.9 | 0.2 | 0.1 |
| 3 | 0.8 | 3.4 | 1.0 | 2.6 | 0.2 |
| 4 | 4.5 | 5.3 | 3.7 | 0.8 | 0.8 |
| 5 | 10.0 | 8.4 | 8.9 | 1.6 | 1.1 |
| 6 | 21.3 | 20.1 | 21.2 | 1.2 | 0.1 |
| 7 | 59.4 | 54.8 | 56.9 | 4.6 | 2.5 |
| 8 | 98.4 | 94.5 | 97.7 | 3.9 | 0.7 |
| 9 | 205.0 | 193.3 | 205.4 | 11.7 | 0.4 |
In addition, a set of real samples prepared by passing wastewater through filters were measured non-destructively by NMR (using the calibration produced from artificial standards in Figure 1) followed by the extraction method; the results are shown in Figure 2. The two methods show a very good correlation, with the exception of sample 17 from which glycerol was also extracted (derived from soap-based products) and sample 20 which was an inhomogeneous sample. The data also shows that the limit of detection of the NMR method is 1 mg/L (compared to 8 mg/L for the solvent extraction method).
Fig. 2 — NMR and solvent extraction results for wastewater samples.
A set of twelve filter papers were prepared using the same sample of wastewater. Again, these were analysed by NMR first followed by solvent extraction; the results are shown in Table 2.
Table 2. Results of NMR repeatability test from the same sample of wastewater
| Method | Repeat Measurements: FOG content, mg | Mean, mg | Standard deviation, mg | |||||||||||
| NMR | 19.7 | 20.8 | 20.9 | 19.4 | 20.0 | 18.9 | 19.4 | 18.2 | 18.4 | 19.1 | 18.6 | 18.3 | 19.3 | 0.9 |
| Soxhlet | 18.6 | 19.3 | 19.7 | 17.5 | 18.1 | 17.8 | 17.7 | 16.8 | 17.2 | 17.1 | 17.3 | 17.2 | 17.9 | 0.9 |
The t and f tests applied to this data (95% confidence interval) show there is a significant difference between the means of the two methods but not the standard deviations; the NMR results are slightly higher than those for solvent extraction which tends to have a low recovery. Furthermore, it is noticeable that the results by the two methods correlate with each other for this composite sample.
© Oxford Instruments 2026
