Disclaimer & Copyright Notices; Optimized for the MS Edge
Source: Info sheets provided during January of 2002 by:
Tamara McFarland BSc., Assistant Project ManagerThe RCAp is performed using highly automated instrumentation and advanced robotics which ensures fast turnaround time and high quality analyses at low cost:
Methods used are those defined by the American Public Health Association and/or the U.S. EPA.
Sampling
The RCAp requires a polyethylene bottle for general water chemistry and a nitric acid preserved polyethylene bottle for trace metals. To prevent losses of ammonia, a sulphuric acid preserved bottle is recommended.Quality Assurance
Precision and accuracy are assured through the evaluation of Certified Reference Materials, method blanks, duplicates and spikes. Secondary QC involves validating the results based on the anion and cation balance.Parameter | Symbol and ionic valence | EQL (Estimated Quantification Limits) | Atomic Number | Atomic Weight/ Molecular Weight |
---|---|---|---|---|
Sodium | Na+ | 0.1 mg/L | 11 | 22.98977 |
Potassium | K+ | 0.1 mg/L | 19 | 39.0983 |
Calcium | Ca2+ | 0.1 mg/L | 20 | 40.08 |
Magnesium | Mg2+ | 0.1 mg/L | 12 | 24.305 |
Hardness as CaCO3 | 0.1 mg/L | |||
Iron | Fe | 0.2 mg/L | 26 | 55.847 |
Manganese | Mn | 0.01 mg/L | 25 | 54.9380 |
Copper | Cu | 0.01 mg/L | 29 | 63.546 |
Zinc | Zn2+ | 0.05 mg/L | 30 | 65.38 |
Alkalinity as CaCO3 | 1 mg/L | |||
Sulphate | SO42- | 2 mg/L | 96.058 | |
Chloride | Cl- | 1 mg/L | 17 | 35.453 |
Reactive Silica as SiO2 | 0.5 mg/L | |||
Nitrate + Nitrite as N | NO3-/ NO2-1 | 0.05 mg/L | 62.005 | |
Ammonia as N | NH3 | 0.05 mg/L | 17.030 | |
o-Phosphate as P | PO43- | 0.01 mg/L | 94.971 | |
Dissolved Organic Carbon as C | DOC | 0.5 mg/l | ||
pH | pH | - | ||
Conductivity (25oC | 1 µmho/cm | |||
Colour | 5 TCU | |||
Turbidity | 0.1 NTU | |||
Bicarbonate as CaCO3 | 1 mg/L | |||
Carbonate as CaCO3 | 1 mg/L | |||
Saturation pH (4oC, 20oC) | - | |||
Langelier Index (4oC, 20oC) | - | |||
Cation Sum | 0.1 meq/L | |||
Anion Sum | 0.1 meq/L | |||
Ion Balance % | - | |||
Total Dissolved Solids (calc'd) | 1 mg/L |
Parameter | Symbol and ionic valence | EQL (Estimated Quantification Limits) | Atomic Number | Atomic Weight/ Molecular Weight |
---|---|---|---|---|
This includes the RCAp parameters plus: | ||||
Nitrate and Nitrite breakdown | - | |||
Aluminum | Al3+ | 0.01 mg/L | 13 | 26.98154 |
Antimony | Sb | 0.002 mg/L | 51 | 121.75 |
Arsenic | As | 0.002 mg/L | 33 | 74.9216 |
Barium | Ba | 0.005 mg/L | 56 | 137.33 |
Beryllium | Be | 0.005 mg/L | 4 | 9.01218 |
Bismuth | Bi | 0.002 mg/L | 83 | 208.9804 |
Boron | B | 0.005 mg/L | 5 | 10.81 |
Cadmium | Cd | 0.0003 mg/L | 48 | 112.41 |
Chromium | Cr | 0.002 mg/L | 24 | 51.996 |
Cobalt | Co | 0.001 mg/L | 27 | 58.9332 |
Lead | Pb | 0.0005 mg/L | 82 | 207.2 |
Molybdenum | Mo | 0.002 mg/L | 42 | 95.94 |
Nickel | Ni | 0.002 mg/L | 28 | 58.70 |
Phosphorus | P | 0.1 mg/L | 15 | 30.97 |
Selenium | Se | 0.002 mg/L | 34 | 78.96 |
Silver | Ag | 0.0003 mg/L | 47 | 107.868 |
Strontium | Sr | 0.005 mg/L | 38 | 87.62 |
Thallium | Tl | 0.0001 mg/L | 81 | 204.37 |
Tin | Sn | 0.002 mg/L | 50 | 118.69 |
Titanium | Ti | 0.002 mg/L | 22 | 47.90 |
Uranium | U | 0.0001 mg/L | 92 | 238.029 |
Vanadium | V | 0.002 mg/L | 23 | 50.9414 |
The Canadian Council of Ministers of the Environment (CCME) guidelines provide remediation criteria for toxic metals. For instance, the following concentrations have been established for commercial or industrial sites: arsenic - 50 mg/kg; cadmium - 20 mg/kg; lead - 1000 mg/kg (PSC- Technical Data Sheet, February 1999).
Analysis
Metals in soils and sediments are routinely determined as "available metals" based upon the digestion technique provided in EPA Method 3050A. Alternative digestion procedures, such as the "total metals" digest are available upon request. Samples are digested with concentrated nitric acid and hydrogen peroxide. The digestate is then diluted to volume and centrifuged in order to segregate any remaining solids. The supernatant is further diluted and analysed using an inductively coupled plasma - mass spectrometer (ICP-MS) and on inductively coupled plasma - optical emission spectrometer (ICP-OES). Results (in mg/kg) are provided for a 22 element suite based upon the original dry weight of the sample.Precision and accuracy are ensured through the evaluation of Certified Reference Materials, method blanks, method duplicates method spikes. Complete quality assurance data will be provided with sample results upon request.
Sampling
A minimum of 100 grams of a representative soil or sediment sample should be collected in a clean glass soil jar. Clean sample containers can be supplied upon request.The Table below illustrates results obtained when a reference sample is analysed using a "total metals" digest and an "available metals" digest.
Analyte | "Total" | "Available" | Reporting Limit* |
---|---|---|---|
Aluminum | 85,000 | 12,000 | 10 |
Antimony | <2 | <2** | 2 |
Arsenic | 19 | 18 | 2 |
Barium | 960 | 290 | 5 |
Beryllium | <5 | <5 | 5 |
Boron4 | N/A | 19 | 5 |
Cadmium | 0.21 | 0.23 | 0.3 |
Chromium | 87 | 23 | 2 |
Cobalt | 14 | 12 | 1 |
Copper | 34 | 33 | 2 |
Iron | 43,000 | 31,000** | 20 |
Lead | 22 | 19 | 0.5 |
Manganese | 340 | 310 | 2 |
Molybdenum | 2.7 | <2 | 2 |
Nickel | 44 | 40 | 2 |
Selenium | <2 | <2 | 2 |
Silver | N/A | 0.5 | 0.5 |
Strontium | 110 | 48 | 5 |
Thallium | 1.0 | 0.2 | 0.1 |
Tin5 | 2 | N/A | 2 |
Uranium | 2.9 | 1.3 | 0.1 |
Vanadium | 210 | 42 | 2 |
Zinc | 160 | 130 | 2 |
** = Low recoveries are probable for these elements. Alternate digest is available upon request to obtain full recoveries.
N/A = not available
Note: The actual amount of variation that is observed for an individual sample will be dependent upon the sample matrix.
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