The distinction matters commercially, and the page's own worked example shows why. An IDL of 0.0008 µg/mL Cr on the instrument becomes a detection limit of 4 ppm on the original sample once the 0.2 g into 1000 mL dilution is accounted for — and a realistic working figure of roughly 16 ppm, four times the IDL. Quoting an instrument detection limit as though it were a method detection limit overstates what the method can do by three orders of magnitude.
The formal MDL procedure is defined in EPA 40 CFR Part 136, Appendix B.
What Is Linearity and Linear Dynamic Range?
Linearity is the range over which instrument response is directly proportional to analyte concentration. The linear dynamic range runs from the limit of quantitation at the bottom to the concentration at which the plot of concentration against response departs from a straight line at the top.
Below the LOQ, the response is real but too imprecise to quantify. Above the upper limit, the detector begins to saturate and the calibration curve rolls over — results in this region read low, and will do so silently unless the range has been established in advance.
Modern ICP-OES instruments typically deliver five to six orders of linear dynamic range, and ICP-MS eight or more. The practical range for a given line is narrower than the instrument's headline figure, because it is bounded by the detection limit for that line at the bottom and by the onset of self-absorption or detector saturation at the top. This is why the linear range is established per line, not per instrument.
Defining ICP Performance Characteristics
The following steps are intended as a practical guide for the determination of an ICP's performance characteristics:
- Read the operating manual and familiarize yourself with the software, key instrumental parameters, and preferred settings before the instrument is installed.
Most instruments are supplied with optimization and wavelength or mass calibration standards that will be used during set-up by the service technician and are intended for use on a regular basis by the operator. Discuss the optimization process with the manufacturer as well as the preferred settings for the key instrumental parameters.
The remaining steps assume that the operator fully understands and is able to perform the optimization process that has been defined by the manufacturer, as well as the spectral limitations of the instrument.
- Select the lines to be studied for each element ("lines" is used in this document to mean either wavelength or mass).
Line selection is based upon spectral interference issues, detection limit requirements, and working range requirements. Select as many lines as possible within practicality for each element. The greater the number of lines, the greater the flexibility.
- Prepare single-element standards over the anticipated working range for each element. The range of standards depends upon the analytical requirements. The following ranges are suggestions only:
- Radial view ICP-OES: 0.0, 1, 10, 100, and 1000 µg/mL
- Axial view ICP-OES: 0.0, 0.1, 1, 10, and 100 µg/mL
- Quadrupole (R~300) mass-filtered ICP-MS: 0, 1, 10, 100, and 1000 ng/mL
This step is important because these data can be used to determine instrument detection limits (IDL), linear working ranges, and spectral characteristics such as background equivalent concentrations (BEC) and spectral interferences. With most modern (if not all) instruments, the spectra obtained for each element at each concentration can be saved for review later. In addition, the software will calculate the IDL and BEC, and the linear regression of each line will establish the linear working range. All of this is typically done for the operator by the software that comes with the instrument. If at all possible, attempt to:
- Use single-element standards that have the trace metal impurities reported on the certificate of analysis. Most chemical standards manufacturers provide this information with their single-element standards. These data are important in identifying direct spectral overlap interferences and in not identifying an impurity as an interference of this type.
- Store all spectra on computer and collect the spectra for all lines of interest on each and every solution. This means that if you are interested in possibly using up to 6 lines for roughly 72 elements, then each solution spectrum totaling 72 × 6 = ~432 lines per solution, and ~432 × 5 = 2160 spectra for each element need to be stored for future reference. Most ICP-MS applications would require far fewer data to be collected due to the reduced number of lines available and/or feasible.
- Wash blank acid solution through the instrument for several minutes "between elements," and always analyze a blank at the beginning of each element concentration series. Look for the presence of the prior element analyzed to confirm that it has been completely washed out of the introduction system.
- Having the data available on a desktop computer is convenient and allows the analyst to construct potential spectra by calling up the element and the anticipated concentration for each element in the analytical sample. Having several lines available makes the job of line selection easy, as well as the estimation of the line's sensitivity and linearity. Constructing these composite spectra from pure single-element solutions eliminates confusion as to the identity of the line. The following example is intended to illustrate the process:
Examples of Spectra
FYI: All spectra were obtained using a concentric glass nebulizer with no problems around salting out or plugging.
The following example is for an application where a submitter has been obtaining minor levels (0.1 to 1.0%) of Cr in an alloy containing roughly equal amounts of Fe and Ni. The laboratory where this alloy is analyzed uses a procedure where 0.2 grams of the sample is dissolved in 5 mL of a 1:1 HNO₃/HCl mixture and diluted to 1000 mL with DI water. The analyst is informed that a limit of detection (LOD = 3SD₀) of 1 ppm Cr based upon the original sample, and the ability to quantify the Cr to within ±10% relative at the 10 ppm level, is an absolute minimum requirement.
The submitter then asks the analyst the usual question: "I need the results tomorrow — can you do it?" The analyst does a quick calculation and determines that, using the most sensitive Cr line and the current procedure, the lowest possible detection limit is 4 ppm, and a more realistic estimation would be ~4 times the IDL, or ~16 ppm. The analyst then pulls up the following spectra, instrument detection limits, and linear regression data, which were obtained on their radial view instrument about four years ago when installed, using pure single-element solutions as described above.
The 205.552 nm Cr line was found to be the most sensitive of the 16 Cr lines originally characterized, with an IDL of 4.0 ppm = [(0.0008 µg/mL Cr IDL) × 1000] / 0.2, based upon original sample size and dilution as described above. However, the spectrum of a 0.1 ppm Cr standard shows significant interference from both Ni and Fe at a concentration of 100 ppm, making the line useless at low ppm Cr levels (see Figures 7.1 and 7.2).