Background concentrations for naturally occurring inorganic chemicals and selected radionuclides in surface and subsurface soil
These tables were originally obtained from Methods for Conducting Risk Assessments and Risk Evaluations at the Paducah Gaseous Diffusion Plant. Volume 1. Human Health, DOE/OR/07-1506&D2. 2000. A more recent DRAFT Methods document is Methods for Conducting Risk Assessments and Risk Evaluations at the Paducah Gaseous Diffusion Plant. Volume 1. Human Health, DOE/LX/07-0107&D1/V1. 2009. This document should be final in 2010. In the meantime, the 2000 report is recommended. The background values presented below are form the more recent release and the values in these tables were developed considering agreements reached between the United States Department of Energy and the regulatory agencies during comment resolution meetings, in the Federal Facility Agreement, and at technical meetings. The human health document appendices contain a series of Action and No Action Risk-based screening values for the various receptors and the provisional background values for groundwater and soil. Finally, the Commonwealth has released a state-wide background table. Because surface water and sediment are transient media in which concentrations and activities can change rapidly, PGDP does not plan to develop surface water and sediment background. Only draft background values for groundwater drawn from the Regional Gravel Aquifer (RGA) and McNairy Formation are currently available. This description will be updated to indicate when these values have been approved.
Further information about the use of background in Ecological Assessments may be found here Methods for Conducting Risk Assessments and Risk Evaluations at the Paducah Gaseous Diffusion Plant. Volume 2. Ecological, DOE/LX/07-0107&D2/V2. 2009.
Analyte | Background Valueb | |
---|---|---|
Surface | Subsurface | |
Inorganic Chemicals (mg/kg)a | ||
Aluminum | 16,045 | 9,732 |
Antimony | 0.21 | 0.21 |
Arsenic | 11 | 4.0 |
Barium | 182 | 78 |
Beryllium | 0.90 | 0.92 |
Cadmium | 0.21 | 0.21 |
Calcium | 8,376 | 1,926 |
Chromium (III) | 25 | 22 |
Chromium (VI)d | --- | --- |
Cobalt | 13 | 8.8 |
Copper | 24 | 12 |
Cyanide (CN-)c | --- | --- |
Iron | 28,657 | 23,698 |
Lead | 35 | 14 |
Magnesium | 2,652 | 1,168 |
Manganese | 701 | 250 |
Mercury | 0.20 | 0.20 |
Nickel | 28 | 15 |
Potassium | 1,005 | 499 |
Selenium | 0.6 | 0.6 |
Silver | 3.0 | 1.9 |
Sodium | 142 | 331 |
Sulfided | --- | --- |
Thallium | 0.21 | 0.45 |
Tind | --- | --- |
Uranium | 7.6 | 7.2 |
Vanadium | 44 | 34 |
Zinc | 82 | 38 |
Radionuclide (pCi/g) | ||
Cesium-137 | 0.50 | 0.074 |
Neptunium-237e | 0.028 | --- |
Plutonium-238e | 0.004 | --- |
Plutonium-239e | 0.018 | --- |
Potassium-40 | 27 | 27 |
Radium-226 | 2.2 | 2.3 |
Strontium-90e | 0 | --- |
Technetium-99 | 0.3 | 0.79 |
Thorium-228 | 2.3 | 2.3 |
Thorium-230 | 2.2 | 2.2 |
Thorium-232 | 2.2 | 2.2 |
Uranium-234 | 1.9 | 1.8 |
Uranium-235 | 0.11 | 0.11 |
Uranium-238 | 1.9 | 1.8 |
Notes: Cells with dashes (---) indicate data are not available or not applicable.
aIncludes inorganic chemicals found on Target Analyte List as defined by EPA in 1988 CLP Statement of Work and RCRA Appendix IX list of constituents.
bValue for use in screening to determine if inorganic chemical or radionuclide detected at naturally occurring concentration in surface or subsurface soil. Details on the derivation of the background concentrations for antimony, beryllium, cadmium, thallium, uranium, and all radionuclides are in DOE 1997a . Details on the derivation of the background concentration for all other inorganic chemicals are in DOE 1996a.
cCyanide is not expected to be naturally occurring in soil at PGDP; background values were not derived.
dData are not adequate to calculate a background concentration in soil for this analyte.
eConcentrations for these radionuclides in subsurface soil were not derived.
Provisional background concentrations for naturally occurring inorganic chemicals and selected radionuclides in filtered and unfiltered groundwater drawn from the RGA and McNairy Formation
Analyte | Over All Observations | Over Wells | ||
---|---|---|---|---|
RGA | McNairy | RGA | McNairy | |
Inorganic Chemicals (mg/L) | ||||
Aluminum | 2.189 | 0.687 | 1.64 | 0.75 |
Aluminum, Dissolved | 0.311 | 0.579 | 0.201 | 0.587 |
Antimony | 0.060 a | 0.060 a | 0.060 a | 0.060 a |
Antimony, Dissolved | 0.060 a | 0.060 a | 0.060 a | 0.060 a |
Arsenic | 0.005 a | 0.005 a | 0.005 a | 0.005 a |
Arsenic, Dissolved | 0.005 a | 0.005 a | 0.005 a | 0.005 a |
Barium | 0.235 | 0.296 | 0.202 | 0.265 |
Barium, Dissolved | 0.200 | 0.268 | 0.179 | 0.266 |
Beryllium | 0.004 a | 0.017 a | 0.004 a | 0.017 a |
Beryllium, Dissolved | 0.004 a | 0.004 a | 0.004 a | 0.004 a |
Cadmium | 0.010 a | 0.010 a | 0.010 a | 0.010 a |
Cadmium, Dissolved | 0.010 a | 0.010 a | 0.010 a | 0.010 a |
Calcium | 41.238 | 38.858 | 40.0 | 39.47 |
Calcium, Dissolved | 38.166 | 38.829 | 35.8 | 40.27 |
Chloride | 91.021 | 19.708 | 89.2 | 20.23 |
Chromium | 0.144 | 0.060 a | 0.134 | 0.060 a |
Chromium, Dissolved | 0.050 a | 0.050 a | 0.050 a | 0.050 a |
Cobalt | 0.045 a | 0.096 | 0.045 a | 0.072 |
Cobalt, Dissolved | 0.045 a | 0.045 a | 0.045 a | 0.045 a |
Copper | 0.036 | 0.057 | 0.034 | 0.033 |
Copper, Dissolved | 0.020 | 0.013 a | 0.018 | 0.013 a |
Fluoride | 0.270 | 0.330 | 0.245 | 0.298 |
Iron | 5.030 | 18.360 | 3.72 | 15.83 |
Iron, Dissolved | 0.267 | 12.372 | 0.164 | 9.446 |
Lead | 0.129 | 0.050 a | 0.250 | 0.050 a |
Lead, Dissolved | 0.098 | 0.050 a | 0.250 | 0.050 a |
Magnesium | 16.262 | 13.418 | 15.7 | 16.457 |
Magnesium, Dissolved | 16.215 | 14.171 | 15.4 | 16.533 |
Manganese | 0.119 | 0.941 | 0.082 | 0.729 |
Manganese, Dissolved | 0.068 | 0.894 | 0.048 | 0.682 |
Mercury | 0.0002 a | 0.0002 a | 0.0002 a | 0.0002 a |
Mercury, Dissolved | 0.0002 a | 0.0002 a | 0.0002 a | 0.0002 a |
Molybdenum | 0.050 a | 0.050 a | 0.050 a | 0.050 a |
Molybdenum, Dissolved | 0.050 a | 0.050 a | 0.050 a | 0.050 a |
Nickel | 0.682 | 0.109 a | 0.682 | 0.109 a |
Nickel, Dissolved | 0.305 | 0.050 a | 0.305 | 0.050 a |
Nitrate as Nitrogen | 15.561 | 1.474 | 13.5 | 1.43 |
Potassium | 5.195 | 55.752 | 4.47 | 64.080 |
Potassium, Dissolved | 4.096 | 51.205 | 3.70 | 58.750 |
Selenium | 0.005 a | 0.005 a | 0.005 a | 0.005 a |
Selenium, Dissolved | 0.005 a | 0.005 a | 0.005 a | 0.005 a |
Silica | 26.401 | 36.0 | 21.1 | 29.4 |
Silver | 0.011 a | 0.050 a | 0.011 a | 0.050 a |
Silver, Dissolved | 0.060 a | 0.050 a | 0.060 a | 0.050 a |
Sodium | 59.450 | 29.2 | 63.5 | 24.92 |
Sodium, Dissolved | 60.433 | 27.98 | 65.7 | 25.90 |
Sulfate | 19.947 | 28.9 | 19.1 | 27.27 |
Thallium | 0.056 a | 0.644 | 0.056 a | 0.255 |
Thallium, Dissolved | 0.056 a | 0.056 a | 0.056 a | 0.056 a |
Uranium | 0.002 a | 0.001 a | 0.002 a | 0.001 a |
Uranium, Dissolved | 0.002 a | 0.001 | 0.002 a | 0.001 |
Vanadium | 0.134 | 0.126 | 0.139 | 0.119 |
Vanadium, Dissolved | 0.134 | 0.126 | 0.131 | 0.107 |
Zinc | 0.054 | 0.142 | 0.025 | 0.104 |
Zinc, Dissolved | 0.049 | 0.116 | 0.026 | 0.080 |
Radionuclides (pCi/L) | ||||
Gross Alpha | 5.8 | 11.9 | 2.36 | 5.3 |
Gross Beta | 13.8 | 144.5 | 7.3 | 125.4 |
Neptunium-237 | 0.8 | 0.5 | 0.21 | 0.13 |
Plutonium-239 | 0.1 | 0.2 | 0.03 | 0.04 |
Radium-226 | 0.6 | 1.2 | 0.10 | 0.29 |
Radon-222 | 626 | 295 | 555.3 | 228.3 |
Technetium-99 | 22.3 | 20.6 | 10.8 | 7.8 |
Thorium-230 | 1.1 | 1.5 | 0.54 | 0.40 |
Total Radium | 1.3 | 0.7 | 0.46 | 0.36 |
Uranium-234 b | 0.7 | 0.3 | 0.7 | 0.3 |
Uranium-235 b | 0.3 | 0.2 | 0.3 | 0.2 |
Uranium-238 b | 0.7 | 0.3 | 0.7 | 0.3 |
Notes: Values taken from the draft Background Concentrations of Naturally Occurring Inorganic Chemicals and Selected Radionuclides in the Regional Gravel Aquifer and McNairy Formation at the Paducah Gaseous Diffusion Plant, Paducah, Kentucky (Unnumbered).
Values for filtered water samples are also available in the aforementioned report.
For all projects where averages within wells over time are considered, the values derived over wells should be used. For all other projects, the values derived over all observations should be used
aBackground value was derived qualitatively over all observations because analyte was never detected or was detected infrequently at a concentration near the analyte's detection limit.
bUranium isotopic concentrations were derived from the mass concentration of uranium.