Soil and sediment analysis plays an important role in environmental monitoring, geochemistry, land assessment, contamination screening, and resource evaluation. Because soils can contain a complex mixture of nutrients, minerals, trace metals, and potentially toxic elements, laboratories require analytical methods that can quantify a broad elemental range with reliable accuracy, precision, and throughput. Elements such as arsenic, cadmium, lead, chromium, nickel, copper, zinc, uranium, thorium, and selected rare earth elements can provide important information about sample origin, environmental impact, and material composition.
This application note examines the use of energy-dispersive X-ray fluorescence spectroscopy (EDXRF) for the analysis of 45 compounds and elements in soil and sediment samples prepared as pressed powder pellets. It focuses on the quantification of major oxides, minor constituents, trace metals, and selected rare earth elements using the Revontium™ Heavy Element edition benchtop EDXRF spectrometer.
Soil matrices are inherently complex. A single sample may contain high concentrations of silicates, aluminum and iron oxides, alkaline and alkaline earth elements, halogens, transition metals, heavy metals, and low-level trace elements. This complexity can create spectral overlaps in XRF analysis, especially when multiple elements are present across a wide concentration range. Accurate quantification therefore depends on optimized excitation conditions, stable sample preparation, robust calibration, and software capable of resolving overlapping peaks.
Another challenge is analytical efficiency. Laboratories often need to screen or quantify many elements in a single workflow without relying on multiple separate methods. A benchtop EDXRF approach can support multi-element analysis with minimal sample preparation, making it useful for routine soil and sediment characterization where speed and consistency are important.
EDXRF is a non-destructive elemental analysis technique that measures characteristic fluorescent X-rays emitted by a sample after excitation by an X-ray source. The resulting spectrum can be used to identify and quantify elements from light major components through heavier trace elements. In this study, measurements were performed using a Revontium Heavy Element edition EDXRF spectrometer equipped with a 50 W X-ray tube, an Ag anode, primary and secondary filters, four high-resolution silicon drift detectors, a spinner, and an automatic sample changer. Measurements were performed under vacuum using an oil-free dry vacuum pump.
The method was developed to quantify 45 compounds and elements, including major oxides such as Na2O, MgO, Al2O3, SiO2, K2O, CaO, TiO2, MnO, and Fe2O3, as well as trace elements such as As, Cd, Pb, Cr, Ni, Cu, Zn, Rb, Sr, Zr, Nb, Mo, Sb, Ba, Th, and U. Selected rare earth elements, including La, Ce, Nd, and Sm, were also included.
The calibration was established using 42 soil and sediment certified reference materials, including GSS, GSR, and GSD geochemical reference materials, along with NIST SRM 2709, 2710, and 2711. Additional Pro-Trace setup samples produced by Malvern Panalytical were also used. Standards and samples were oven dried, pulverized in a planetary ball mill with a wax/styrene additive, and pressed into pellets using a hydraulic press.
Five optimized measurement conditions were used to excite different groups of elements. These conditions covered light elements such as Na, Mg, Al, and Si; elements including P, S, Cl, K, Ca, Sc, Ti, and V; transition metals such as Cr, Mn, Fe, Co, Cu, Ni, and Zn; heavier trace elements including As, Se, Rb, Sr, Y, Zr, Mo, W, Pb, Bi, Th, and U; and additional elements such as Cd, Sn, Sb, Te, Cs, Ba, La, Ce, Nd, and Sm. The total measurement time per sample was 21 minutes, with the option to adjust measurement time depending on analytical requirements.
The Revontium EDXRF approach is relevant for laboratories that need broad elemental coverage from a single prepared soil or sediment pellet. The combination of multiple silicon drift detectors, vacuum measurement conditions, optimized filters, sample spinning, and spectral deconvolution supports analysis of complex matrices containing both high-concentration oxides and trace-level metals. This makes the technique applicable to environmental laboratories, geochemical studies, mining and exploration workflows, and routine material characterization where fast multi-element screening is required.
The full application note provides detailed calibration information, detection limits, and accuracy results for the individual compounds and elements evaluated. It also explains how measurement conditions were selected and how the method can be adapted when lower limits of detection are required for specific elements.
Register to download the full application note and review the complete methodology, calibration data, detection limits, and accuracy results for EDXRF analysis of soils and sediments using Revontium.
Soil contains a wide variety of compounds and elements. This can range from nutrients like sulfates and phosphates to toxic elements like arsenic or cadmium. The destination of a location can be determined based on the elemental composition of soil. This application note demonstrates that Revontium, a high-performance benchtop energy dispersive X-ray fluorescence spectrometer (EDXRF), can analyze major, minor and trace elements in soils and sediments, prepared as pressed powders. In this study an application method is set up for quantifying 45 compounds, including a few rare earth elements (REE) present in soils and sediments.
Measurements were performed using a Revontium™ Heavy Element edition energy-dispersive XRF spectrometer, equipped with an X-ray tube (50 W, 5 mA, 60 kV, Ag anode), primary and secondary filters, four high-resolution silicon drift detectors, a spinner, and a sample changer for automatic batch measurements. All measurements were performed in vacuum by using an oil-free (dry) vacuum pump.
Forty-two soil and sediment certified reference materials (CRM) were used to create the application and included the GSS-, GSR- and GSD-series of geochemical reference materials (Institute of Geophysical and Geochemical Prospecting, PRC) together with NIST SRM 2709, 2710 and 2711 (National Institute of Standards and Technology, USA). Also, four Pro-Trace set-up samples were used, that were produced by Malvern Panalytical in Nottingham. The standards were analyzed in the form of pressed powder pellets. The standards and samples were oven dried and then pulverized in a planetary ball mill together with 25% wax/styrene additive. The additive acts as a binder and a grinding agent, resulting in a uniform grain-size of smaller than 40 µm. Fifteen grams of the mixture was pressed into pellets using a hydraulic press operated at 20 tons pressure.
Five measurement conditions were used to quantify 45 elements in the standards and samples, each one optimizing the excitation of a specific group of elements (Table 1). The total measurement time per sample was only 21 minutes. The measurement time for each condition can be optimized according to specific needs.
The SuperQ v7 software features a powerful deconvolution algorithm, which analyzes the sample spectrum and determines the net intensities of element peaks, even when they overlap one another. This is essential to perform accurate trace element analysis. For the elements P, Cl and Cd, a region of interest (ROI) was used to determine the intensities instead of the traditional deconvolution method.
In this study, mercury was not analyzed because this element is volatile in the samples.
| Elements | kV | mA | Medium | Primary Filter | Secondary Filter | Measuring time (min) |
|---|---|---|---|---|---|---|
| Na, Mg, Al, Si | 4 | 5.000 | Vacuum | none | none | 1 |
| P, S, Cl, K, Ca, Sc, Ti, V | 12 | 0.800 | Vacuum | Al-thin | none | 1 |
| Cr, Mn, Fe, Co, Cu, Ni, Zn | 20 | 0.700 | Vacuum | Al-thick | none | 2 |
| Ga, Ge, As, Se, Br, Nb, Rb, Sr, Y, Zr, Mo, W, Pb, Bi, U, Th | 60 | 0.833 | Vacuum | Ag | polymer | 2 |
| Cd, Sn, Sb, Te, Cs, Ba, La, Ce, Nd, Sm | 60 | 0.833 | Vacuum | Cu | polymer | 15 |
Figures 1 and 2 show the resulting calibration graphs for MgO and La in the soil and sediment CRMs, respectively. The graphs show very good correlation between the certified concentrations and the measured intensities.
Detailed calibration results for all analyzed compounds and trace elements are listed in Table 2. The RMS (Root Mean Square) value is equivalent to 1 sigma standard deviation.
Detection limits (LLD) for the trace elements are obtained through 20 repeat measurements on a blank reference material, including loading and unloading of the sample between measurements. The LLD values are calculated based on the application time listed in Table 1.
| Compound | Unit | Concentration range | RMS | Correlation coefficient | LLD |
|---|---|---|---|---|---|
| Na2O | wt% | 0.04 - 3.50 | 0.20 | 0.993 | N.A. |
| MgO | wt% | 0.12 - 3.40 | 0.43 | 0.996 | N.A. |
| Al2O3 | wt% | 2.84 - 29.26 | 1.41 | 0.970 | N.A. |
| SiO2 | wt% | 32.69 - 88.89 | 2.95 | 0.987 | N.A. |
| P2O5 | wt% | 0.030 - 0.340 | 0.057 | 0.945 | N.A. |
| SO3 | wt% | 0.023 - 0.600 | 0.071 | 0.931 | N.A. |
| Cl | ppm | 30 - 290 | 52 | 0.631 | 7.8 |
| K2O | wt% | 0.125 - 5.190 | 0.071 | 0.999 | N.A. |
| CaO | wt% | 0.095 - 8.270 | 0.269 | 1.000 | N.A. |
| Sc | ppm | 2 - 898 | 11.6 | 0.997 | 5.6 |
| TiO2 | wt% | 0.210 – 3.360 | 0.035 | 1.000 | N.A. |
| V | ppm | 16.5 - 247 | 9.9 | 0.997 | 3.3 |
| Cr | ppm | 7.6 - 370 | 18 | 0.993 | 1.5 |
| MnO | wt% | 0.028 - 1.300 | 0.005 | 0.997 | N.A. |
| Fe2O3 | wt% | 1.460 - 18.760 | 0.188 | 0.999 | N.A. |
| Co | ppm | 2.6 – 28.0 | 7.5 | 0.943 | 0.3 |
| Ni | ppm | 2.7 - 276 | 5.4 | 0.995 | 0.4 |
| Cu | ppm | 4.1 - 2950 | 3.4 | 1.000 | 0.5 |
| Zn | ppm | 16 - 6952 | 5.7 | 1.000 | 0.5 |
| Ga | ppm | 6.4 – 39.3 | 0.9 | 0.994 | 0.8 |
| Ge | ppm | 0.13 – 3.1 | 0.5 | 0.975 | 0.6 |
| As | ppm | 2 - 626 | 2.1 | 1.000 | 0.4 |
| Se | ppm | 0 - 999 | 0.1 | 1.000 | 0.3 |
| Br | ppm | 1.5 – 7.2 | 0.6 | 0.960 | 0.2 |
| Rb | ppm | 9.2 - 470 | 2.7 | 1.000 | 0.2 |
| Sr | ppm | 24.4 – 525.0 | 9.5 | 1.000 | 0.2 |
| Y | ppm | 8.3 – 67 | 2.6 | 1.000 | 0.2 |
| Zr | ppm | 70 - 250 | 10.8 | 0.999 | 0.2 |
| Nb | ppm | 6.8 - 95 | 1.6 | 0.998 | 0.1 |
| Mo | ppm | 0.3 - 92 | 0.6 | 0.999 | 0.2 |
| Cd | ppm | 0.1 - 41.7 | 0.8 | 1.000 | 0.3 |
| Sn | ppm | 1.4 – 3.7 | 0.7 | 1.000 | 0.4 |
| Sb | ppm | 0.2 - 60.0 | 0.6 | 0.999 | 0.4 |
| Te | ppm | 0.1 – 4 | 0.4 | 0.875 | 0.3 |
| Cs | ppm | 1.4 – 849 | 1.4 | 1.000 | 0.9 |
| Ba | ppm | 42 – 1210 | 24.3 | 0.999 | 1.6 |
| La | ppm | 1.3 – 164 | 2.1 | 0.998 | 1.0 |
| Ce | ppm | 3.5 – 400 | 3.2 | 0.999 | 1.0 |
| Nd | ppm | 1.4 – 210 | 6.0 | 0.985 | 1.9 |
| Sm | ppm | 0.2 – 966 | 5.1 | 1.000 | 4.5 |
| W | ppm | 0.52 - 126 | 2.2 | 0.996 | 1.8 |
| Pb | ppm | 13 - 5532 | 10.7 | 0.999 | 0.2 |
| Bi | ppm | 1.0 – 50.0 | 0.7 | 0.998 | 0.3 |
| Th | ppm | 5.0 – 70.0 | 3.3 | 0.982 | 0.3 |
| U | ppm | 5.0 – 70.0 | 2.0 | 1.000 | 0.2 |
To evaluate the accuracy of the method, certified reference material GSS5 was analyzed. Each sample was measured twenty times consecutively. For each element in the sample, the average concentration and standard deviation (1 sigma) of the measurements were compared with the certified value reported on the certificate (see Table 3). The results show excellent accurate results for all elements, and especially at low concentrations in the complex samples with many line overlaps.
The concentration of Cd and Sm in the GSS5 sample are below the limit of quantification (LoQ) when using the 21 minutes measuring time. When the measurement time is longer for those elements, the LoQ will also be lower. For example, when the measuring time of the last condition in Table 1 is increased to 60 minutes, the LLD for Cd is reduced to 0.15 ppm, resulting in a LoQ of 0.5 ppm.
| Compound | Unit | Certified concentration | Measured concentration | Measured RMS |
|---|---|---|---|---|
| Na2O | wt% | 0.12 | 0.22 | 0.005 |
| MgO | wt% | 0.61 | 0.63 | 0.005 |
| Al2O3 | wt% | 21.58 | 21.52 | 0.008 |
| SiO2 | wt% | 52.57 | 50.01 | 0.017 |
| P2O5 | wt% | 0.09 | 0.09 | 0.006 |
| SO3 | wt% | 0.10 | 0.10 | 0.013 |
| Cl | ppm | 76 | 92 | 5 |
| K2O | wt% | 1.50 | 1.46 | 0.005 |
| CaO | wt% | 0.95 | 0.90 | 0.001 |
| Sc | ppm | 17 | 10 | 1 |
| TiO2 | wt% | 0.70 | 1.10 | 0.002 |
| V | ppm | 166 | 163 | 2 |
| Cr | ppm | 118 | 136 | 0.6 |
| MnO | wt% | 0.18 | 0.18 | 0.001 |
| Fe2O3 | wt% | 12.62 | 12.76 | 0.004 |
| Co | ppm | 12.3 | 36.4 | 0.1 |
| Ni | ppm | 40 | 40 | 0.2 |
| Cu | ppm | 144 | 141 | 0.3 |
| Zn | ppm | 494 | 496 | 0.3 |
| Ga | ppm | 31.7 | 29.0 | 0.3 |
| Ge | ppm | 2.6 | 1.2 | 0.2 |
| As | ppm | 412 | 418 | 0.6 |
| Se | ppm | 1.6 | 0.3 | 0.1 |
| Br | ppm | 1.8 | 2.6 | 0.1 |
| Rb | ppm | 117 | 117 | 0.1 |
| Sr | ppm | 41.5 | 41.8 | 0.1 |
| Y | ppm | 21 | 21 | 0.1 |
| Zr | ppm | 272 | 276 | 0.1 |
| Nb | ppm | 22.6 | 21.1 | 0.1 |
| Mo | ppm | 4.6 | 4.6 | 0.1 |
| Cd | ppm | 0.5 | < 0.9 | NA |
| Sn | ppm | 17.7 | 19.3 | 0.1 |
| Sb | ppm | 35.4 | 34.7 | 0.1 |
| Te | ppm | 0.4 | 3.4 | 0.1 |
| Cs | ppm | 15 | 12 | 0.1 |
| Ba | ppm | 296 | 296 | 0.5 |
| La | ppm | 36 | 36 | 0.4 |
| Ce | ppm | 91 | 90 | 0.6 |
| Nd | ppm | 24 | 20 | 1.7 |
| Sm | ppm | 4 | < 15 | NA |
| W | ppm | 33.5 | 31.5 | 1.9 |
| Pb | ppm | 552 | 579 | 0.4 |
| Bi | ppm | 41 | 40 | 0.2 |
| Th | ppm | 22.7 | 18.9 | 0.2 |
| U | ppm | 6.5 | 4.0 | 0.1 |
The results clearly demonstrate the capability of Revontium for the analysis of 45 compounds and trace elements in soils and sediments. One measurement will give a full overview of what the composition is of the sample. The high-resolution and outstanding sensitivity of the four detectors combined with powerful software deconvolution algorithms in the SuperQ software make it possible to quantify complex soil samples with a high number of compounds and trace elements in an accurate and precise way.