Table 915-1 CLEANUP CONCENTRATIONS | ||
Contaminant of Concern | Concentrations | |
Soil TPH (total volatile [C6-C10] and extractable [C10-C36] hydrocarbons) | 500mg/kg | |
Soils and Groundwater - liquid hydrocarbons including condensate and oil | below visual detection limits | |
Soil Suitability for Reclamation | ||
Electrical conductivity (EC) (by saturated paste method)1,2 | <4mmhos/cm | |
Sodium adsorption ratio (SAR) (by saturated paste method)1,2,3 | <6 | |
pH (by saturated paste method)1,2 | 6-8.3 | |
boron (hot water soluble soil extract)1,2,3 | 2mg/l | |
Organic Compounds in Groundwater4 | ||
Benzene | 5µg/l | |
toluene5 | 560 to 1,000µg/l | |
Ethylbenzene | 700µg/l | |
xylenes (sum of o-, m- and p- isomers = total xylenes)5 | 1,400 to 10,000µg/l | |
naphthalene | 140µg/l | |
1,2,4-trimethylbenzene | 67µg/l | |
1,3,5-trimethylbenzene | 67µg/l | |
Groundwater Inorganic Parameters4 | ||
total dissolved solids (TDS)1 | <1.25 X local background | |
chloride ion1 | 250mg/l or <1.25 X local background | |
sulfate ion1 | 250mg/l or <1.25 X local background | |
Residential Soil Screening Level Concentrations (mg/kg)7 | Protection of Groundwater Soil Screening Level Concentrations (mg/kg) Risk Based (R) and MCL Based (M)7,8 | |
Organic Compounds in Soils6, 9, 10 | ||
benzene | 1.2 | 0.0026 (M) |
toluene | 490 | 0.69 (M) |
ethylbenzene | 5.8 | 0.78 (M) |
xylenes (sum of o-, m- and p- isomers = total xylenes) | 58 | 9.9 (M) |
1,2,4-trimethylbenzene | 30 | 0.0081 (R) |
1,3,5-trimethylbenzene | 27 | 0.0087 (R) |
acenaphthene | 360 | 0.55 (R) |
anthracene | 1800 | 5.8 (R) |
benz(a)anthracene | 1.1 | 0.011 (R) |
benzo(b)fluoranthene | 1.1 | 0.3 (R) |
benzo(k)fluoranthene | 11 | 2.9 (R) |
benzo(a)pyrene | 0.11 | 0.24 (M) |
chrysene | 110 | 9 (R) |
dibenzo(a,h)anthracene | 0.11 | 0.096 (R) |
fluoranthene | 240 | 8.9 (R) |
fluorene | 240 | 0.54 (R) |
indeno(1,2,3-cd)pyrene | 1.1 | 0.98 (R) |
1-methylnaphthalene | 18 | 0.006 (R) |
2-methylnaphthalene | 24 | 0.019 (R) |
naphthalene | 2 | 0.0038 (R) |
pyrene | 180 | 1.3 (R) |
Metals in Soils1, 6, 9, 10, 11 | ||
arsenic | 0.68 | 0.29 (M) |
barium | 15000 | 82 (M) |
cadmium | 71 | 0.38 (M) |
chromium (VI) | 0.3 | 0.00067 (R) |
copper | 3100 | 46 (M) |
lead | 400 | 14 (M) |
nickel | 1500 | 26 (R) |
selenium | 390 | 0.26 (M) |
silver | 390 | 0.8 (R) |
zinc | 23000 | 370 (R) |
Table 915-1 (continued) footnotes
1 The Director will consider site-specific background concentrations or reference levels in native soils and Groundwater.
2 Soil suitability thresholds for electrical conductivity ("EC"), pH, and sodium adsorption ratio ("SAR") in soils are based on use of saturated paste preparation methods, followed by analysis. Soil suitability thresholds for available boron are based on hot water soluble (or DPTA/sorbitol) extraction followed by analysis. Methods for preparation and analysis of the soil suitability parameters can be found in Soil, Plant, and Water Reference Methods for the Western Region, as incorporated by reference in Rule 901.b.
3 With the Director's prior approval, SAR levels and the concentration for hot water soluble boron may be modified based on land use, depth, or characteristics of the vegetative community.
4 Concentrations for Groundwater are taken from WQCC Regulation 41, as incorporated by reference in Rule 901.b.
5 For toluene and xylenes (total), the first number in the range is a strictly health-based value based on the WQCC's established methodology for human health-based standards. The second number in the range is a maximum contaminant level ("MCL"), established under the federal Safe Drinking Water Act which has been determined to be an acceptable level of this Chemical in public water supplies, taking treatability and laboratory detection limits into account. The WQCC intends that control requirements for this Chemical be implemented to attain a level of ambient water quality that is at least equal to the first number in the range except as follows:
6 Concentrations for organic compounds and metals in soils are taken from the November 2020 EPA Regional Screening Levels ("EPA RSLs") for Chemical Contaminants at Superfund Sites, as incorporated by reference in Rule 901.b.
7 If there is no pathway for communication with Groundwater, then residential soil screening levels apply for organic compounds and metals. If the Director determines that a pathway to Groundwater exists, then the protection of Groundwater soil screening levels will apply, secondary to actual measured concentrations of the contaminants of concern in Groundwater.
8 The letter "(R)" following a protection of Groundwater soil screening level indicates the concentration is derived from a risk-based approach. The letter "(M)" following a protection of Groundwater soil screening level indicates the concentration is derived from the drinking water MCL.
9 If the method detection limit ("MDL") or practical quantitation limit ("PQL") for a pollutant is higher (less stringent) than a threshold concentration listed in Table 915-1, the Director may allow an Operator to substitute the MDL or PQL for the concentration listed in Table 915-1.
10 The risk based cleanup concentrations for organic compounds in soils shown in Table 915-1 are taken from the EPA RSLs, as incorporated by reference in Rule 901.b, tables for Target Risk ("TR") = 1x10-6 and Target Hazard Quotient ("THQ")=0.1. The risk-based cleanup concentrations for metals in soils shown in Table 915-1 are taken from the EPA RSLs, as incorporated by reference in Rule 901.b, tables for TR=1X10-6 and THQ=1. The EPA RSL Frequently Asked Questions pages suggest that the THQ=0.1 tables are appropriate when more than 1 compound of concern is to be considered as present or likely to be present as is typical in soils impacted with organic compounds in Spills or Releases of produced water or liquid hydrocarbons.
11 The Director will consider Residential Soil Screening Level Concentrations up to 1.25 times site specific background levels for metals in soil.
2 CCR 404-1-915