USGS-NWQL: I-1472-87: Metals in Water by ICP
Official Method Name
|
Metals, Atomic Emission Spectrometry, Inductively Coupled Plasma (ICP) |
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Current Revision
| 1987 |
Media
|
WATER |
Instrumentation
|
Inductively Coupled Plasma - Atomic Emission Spectroscopy |
Method Subcategory
|
Inorganic |
Method Source
|
|
Citation
|
Methods for the Determination of Inorganic Substances in Water and Fluvial Sediments, Techniques of Water-Resources Investigations of the United States Geological Survey, Book 5, Chapter A1 Edited by Marvin J. Fishman and Linda C. Friedman |
Brief Method Summary
|
All metals are determined simultaneously on a single sample by a direct-reading emission spectrometric method using an inductively coupled argon plasma as an excitation source. Samples are pumped into a crossflow pneumatic nebulizer, and introduced into the plasma through a spray chamber and torch assembly. Each analysis is determined on the basis of the average of three replicate integrations, each of which is background corrected by a spectrum shifting technique except for lithium (670.7 nm) and sodium (589.0 nm). A series of five mixed-element standards and a blank are used for calibration. Detection limits vary by species; see the published method for detection limits for each species. |
Scope and Application
|
This method is used only for the determination of dissolved metals in water samples that have a measured specific conductance of less than 2,000 uS/cm at 25 deg C. Samples containing analyte concentrations greater than the maximum concentration limit can be analyzed for calcium, magnesium, silica, and sodium if the sample is diluted and if, after dilution, the specific conductance is less than 2,000 uS/cm. Trace metals also can be determined after appropriate dilution in samples that have a measured specific conductance greater than 2,000 uS/cm; however, detection levels and sensitivity will change proportionally. This modified method was implemented in the National Water Quality Laboratory In August 1987. |
Applicable Concentration Range
|
1 - 10000 (undiluted) |
Interferences
|
Several interelement interference effects have been evaluated. Interelement correction factors are programmed into the Thermo Jarrell-Ash system software, and corrections are automatically applied internally to the data before they are printed. Samples containing high dissolved solids show a variety of unidentified interference effects. Therefore, analyses need to be limited to samples with a specific conductance of 2,000 uS/cm or less. |
Quality Control Requirements
|
Method blanks, reagent spikes, surrogate spikes, certified reference material samples, continuing calibration verification standards, field blanks, field replicates, matrix spikes and matrix spike duplicates, quarterly control samples and Branch of Quality Assurance samples are analyzed. Data from these are compiled to continually monitor the QA/QC of the analysis. Each analyst must undergo technical and ethics training, perform an initial demonstration of capability, and annually demonstrate continuing capability on an analysis. Additional QA/QC practices may be added. |
Sample Handling
|
Method blanks, reagent spikes, surrogate spikes, certified reference material samples, continuing calibration verification standards, field blanks, field replicates, matrix spikes and matrix spike duplicates, quarterly control samples and Branch of Quality Assurance samples are analyzed. Data from these are compiled to continually monitor the QA/QC of the analysis. Each analyst must undergo technical and ethics training, perform an initial demonstration of capability, and annually demonstrate continuing capability on an analysis. Additional QA/QC practices may be added. |
Maximum Holding Time
|
180 days from sampling |
Relative Cost
|
Less than $50 |
Sample Preparation Methods
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