Target Analyte Metals (Heavy Metals) and Cyanide
This Fact Sheet is presented by the U. S. Environmental Protection Agency, Region III (EPA) to assist in the selection of analytical parameters and the associated Quality Assurance and Quality Control (QA/QC) procedures to be utilized in Phase II Environmental Assessments under the U.S. Environmental Protection Agency (EPA) Brownfields initiative. This fact sheet is presented for informational purposes only, and should not be construed as a federal policy or directive. The Brownfields Coordinator for this region may be reached at 215-814-5000.
LIST OF TARGET ANALYTE METALS AND CYANIDE
- Aluminum
- Antimony
- Arsenic
- Barium
- Beryllium
- Cadmium
- Calcium
- Chromium (Total)
- Chromium (Hexavalent)
- Cobalt
- Copper
- Iron
- Lead
- Manganese
- Magnesium
- Mercury
- Nickel
- Potassium
- Selenium
- Silver
- Sodium
- Thallium
- Vanadium
- Zinc
- Cyanide (Total)
- Cyanide (Amenable)
ANALYSIS METHODS
Please note that the methods listed below are EPA approved and the most commonly used by EPA and their contractors. However, they are not the only methods for the analysis of metals and cyanide. In addition, these are not drinking water test methods.
| METHOD | APPLICABLE MATRICES |
|---|---|
| EPA 200 Series (1) | Aqueous |
| EPA SW-846 Metals Digestion 3000 Series Analysis 7000 Series & 6010 (2) Cyanide 9010 or 9020 (2) | Aqueous, Soil/Sediment, & Waste |
| EPA CLP Statement Of Work 3/90 | Aqueous & Soil/Sediment |
- U.S. Environmental Protection Agency (EPA). 1983. Test Methods for the Chemical Analysis of Water and Wastes. Washington, D.C. March.
- EPA. 1986. Test Methods for Evaluating Solid Waste. SW-846. Washington, D.C. September.
COLLECTION MEDIA/VOLUME
Listed below are the EPA-recommended preservation and holding times as well as suggested glassware.
| MATRIX | GLASSWARE | VOLUME | PRESERVATIVE | HOLDING TIME |
|---|---|---|---|---|
| Soil/Sediment | 8-oz soil jar | 1 8-oz jar | ice to 4º C | 28 days for metals; 14 days for cyanide; 24 hours for hexavalent chromium |
| Aqueous | 1 liter polypropylene bottle | 1 L bottle | metals: HNO3 to pH <2 & ice to 4º C, cyanide; NaOH to pH >12 & ice to 4º C, hexavalent chromium; ice to 4º C |
28 days
14 days 24 hours |
| Waste | 8-oz wide mouth jar | 1 8-oz jar | none required (ice preferred) |
none (try not to exceed 14 days for cyanide) |
MINIMUM LABORATORY QUALITY CONTROL MEASURES
The laboratory should have Standard Operating Procedures available for review for the metals and cyanide analyses and for all associated methods needed to complete the volatile analysis, such as total solids, instrument maintenance, sample handling, and sample documentation procedures. In addition, the laboratory should have a Laboratory Quality Assurance/Quality Control Statement available for review which includes all key personnel qualifications.
| QC TYPE | FREQUENCY OF ANALYSIS | ACCEPTABLE LIMITS |
|---|---|---|
| Initial Calibration | Prior to analysis of samples (minimum three concentration levels for every compound and an instrument blank) | Correlation Coefficient for all analyses should be > 0.995, ICP
analysis should include interference checks, and serial dilutions,
all furnace results should be acquired in duplicate and at least one
cyanide standard must be extracted with the samples Blank concentration should not exceed twice the instrument detection limit |
| Continuing Calibration | Once per 10 samples (mid-level standard containing all compounds) and a continuing calibration blank | Within 10% of true value (20% for cyanide and mercury) Blank concentration should not exceed twice the instrument detection limit |
| Method Blank | Once per digestion or extraction set | See method for allowable limits |
| Matrix Spikes | One per set or per 20 samples | 75-125% |
| Duplicates | One per set or per 20 samples |
MINIMUM DATA PACKAGE REQUIREMENTS
- Sample results in a tabular form (if soil or sediment) reported on a dry weight basis.
- Report % moisture or % solids for all soil and sediment samples.
- Report sample volumes or weights, as well as any dilution factors, for each sample analysis.
- Returned copy of the chain of custody form sent with the samples with laboratory receipt acknowledgment, and the internal or laboratory chain of custody forms.
- Method blank results.
- Initial and continuing calibration data summary forms, including ICP interference forms and ICP serial dilution forms.
- Matrix spike recovery tables, including laboratory recovery QC limits, and duplicate relative percent difference QC limits.
- Date samples were analyzed, on a separate sheet, or results page.
- Optional: sample, standard and blank instrument printouts, instrument run logs, digestion logs, and total solids logs.
Note: The optional QC must be maintained by laboratory for at least one year for possible future QC audits.
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