Unless otherwise specified in the RSRs, polluted soil at a release area shall be remediated so that the concentration of a substance in such soil is equal to or less than:
Except as otherwise specified in the RSRs, polluted soil at a release area shall be remediated so that the concentrations of substances in such soil are equal to or less than the residential direct exposure criteria .
The provisions of this subdivision do not apply to soil polluted with PCBs.
Soil at a release area polluted with metals, petroleum hydrocarbons, or semi-volatile organic substances is not required to be remediated to the direct exposure criteria for those substances, provided such pollution is the result of
Soil polluted with pesticides at a release area as a result of the application of pesticides is not required to be remediated to the direct exposure criteria for such pesticides, provided that a determination has been made that such pesticides are present solely as a result of the application of pesticides and:
Provided that NAPL is not present in the release area above the seasonal high water table, as determined in accordance with subdivision (4) of this subsection, substances in soil in a GB area may be remediated to a concentration at which the results of a TCLP or SPLP analysis of each substance is equal to or less than the groundwater protection criteria:
Geologic Material | Infiltration Rate (feet/year) |
Stratified Drift | 2.0 |
Till | 0.5 - 1.0 |
Lacustrine Deposits | 0.4 |
Term | Description | Value | Units |
DF | Release-specific dilution factor | substance-specific | unitless |
K | Hydraulic conductivity of the unconsolidated aquifer underlying the release area | calculated | ft/year |
i | Horizontal hydraulic gradient | calculated | ft/ft |
d | Aquifer mixing zone default value of 3 feet or a release- specific value calculated using: | 3, or as otherwise calculated | ft |
d[ALPHA] | Aquifer thickness | as determined from boring logs | ft |
I | Infiltration rate, as identified in section 22a-133k-2(c)(3)(B) (iii)(IV) of the RSRs | calculated | ft/year |
L | Length of the release area parallel to the direction of groundwater flow | as measured | ft |
Fadj | Background concentration for groundwater divided by the groundwater protection criteria for the subject substance or, where the background concentration for groundwater cannot be quantified, one half the laboratory reporting limit for the subject substance divided by the groundwater protection criteria for the subject substance | calculated | unitless |
Terms | Description | Units | Value |
CNAP | Concentration of an organic substance at which or above which such substance may be present in a non-aqueous phase | mg/kg | calculated |
S | Effective solubility | mg/L | substance-specific |
Pb | Dry soil bulk density | kg/L | 1.5 or the lowest value measured at the subject release area |
Kd | Soil-water partition coefficient, which is calculated using Kd = Koc*foc | L/kg | calculated |
Koc | Soil organic carbon-water partition coefficient | L/kg | substance-specific |
foc | Fraction organic carbon of soil | g/g | 0.006 or the lowest value measured at the subject release area |
[THETA] w | Water-filled soil porosity Lwater/Lsoil | Lwater/Lsoil | 0.15 for unsaturated soil or 0.43 for saturated soil |
[THETA] a | Air-filled soil porosity Lair/Lsoil | Lair/Lsoil | 0.28 for unsaturated soil or 0.0 for saturated soil |
H' | Henry's law constant (dimensionless) | unitless | H x 41 where 41 is a conversion factor |
H | Henry's law constant | atm- m3/mol | substance-specific |
Polluted soil at a release area above the seasonal high water table is not required to be remediated to the pollutant mobility criteria, provided that:
Polluted soil at a release area polluted with substances, other than volatile organic substances, that exceed DEC or PMC is not required to be remediated to the pollutant mobility criteria, provided that at such release area:.
Soil at a release area polluted with metals, petroleum hydrocarbons, or semi-volatile organic substances is not required to be remediated to the pollutant mobility criteria, provided such pollution is the result of
Soil polluted with pesticides at a release area as a result of the application of pesticides at such release area is not required to be remediated to the pollutant mobility criteria, provided that a determination has been made that such pesticides are present solely as a result of the application of pesticides and:
With respect to a substance, except PCBs, for which direct exposure criteria are specified in Appendix A of the RSRs or approved in writing by the commissioner pursuant to subsection (b)(7) of this section, the commissioner may approve or deny in writing a request for an alternative release-specific direct exposure criteria or an alternative method for determining compliance with such criteria.
With respect to substances for which pollutant mobility criteria are specified in Appendix B of the RSRs or approved by the commissioner pursuant to subsection (c)(6) of this section, the commissioner may approve or deny in writing a request for an alternative release-specific pollutant mobility criteria or an alternative method for determining compliance with such criteria. No request shall be approved unless it is demonstrated to the commissioner's satisfaction that the application of such alternatives:
With respect to substances for which pollutant mobility criteria are specified in Appendix B of the RSRs or approved by the commissioner pursuant to subsection (c)(6) of this section, the commissioner may approve or deny in writing a request for an alternative release-specific dilution or dilution attenuation factor. No request shall be approved unless it is demonstrated to the commissioner's satisfaction that the application of such dilution attenuation factor :
For any request for approval of alternative pollutant mobility criteria or alternative dilution or dilution attenuation factor specified in this subdivision, alternative groundwater criteria shall not be used for the same substance for which alternative soil criteria is requested.
With respect to substances for which pollutant mobility criteria are specified in Appendix B of the RSRs, alternative release-specific pollutant mobility criteria for a particular release area may be calculated by an LEP in accordance with Appendix H of the RSRs and used at a release area, provided that:
Unless an alternative method for determining compliance with direct exposure criteria has been approved in writing by the commissioner pursuant to subsection (d)(2) of this section, compliance with direct exposure criteria for each substance is achieved when either:
Unless an alternative method for determining compliance with pollutant mobility criteria has been approved in writing by the commissioner pursuant to subsection (d)(3) of this section, compliance with pollutant mobility criteria for each substance is achieved when either:
Compliance when remediating to the background concentration for a given substance in soil is achieved when:
Geographically-extensive polluted fill present at a parcel may be eligible for a variance from compliance with the pollutant mobility criteria in accordance with subparagraph (B) or (C) of this subdivision, provided that:
A variance for widespread polluted fill in accordance with this subdivision may be certified in writing by an LEP, provided such LEP determines that a parcel complies with the eligibility requirements in subparagraph (A) of this subdivision and the LEP demonstrates that the following requirements have been satisfied:
The commissioner may approve or deny in writing a request for a variance under this subsection. No request shall be approved unless such request demonstrates to the commissioner's satisfaction the eligibility requirements in subparagraph (A) of this subdivision and the requirements of this subparagraph have been satisfied. A request for such variance shall be submitted to the commissioner in accordance with section 22a-133k-l(g) of the RSRs, and shall also include:
A release area may be eligible for a variance from compliance with the direct exposure criteria, the pollutant mobility criteria, or both, under this subdivision through the use of an engineered control, provided that:
A variance from compliance with the direct exposure criteria may be available when an engineered control is used at a release area, provided an LEP certifies to the commissioner, in accordance with section 22a-133k-l(g) of the RSRs, that the eligibility requirements of subparagraph (A) of this subdivision and the following requirements have been satisfied:
In addition, if a variance under this subclause includes volatile organic substances, such engineered control shall be designed, constructed, and will be maintained, to ensure that any soil vapor migrating from the subject release area complies with all applicable volatilization criteria in accordance with section 22a-133k-3(c)(3) of the RSRs;
After an engineered control has been certified by an LEP or approved by the commissioner pursuant to this subdivision, the following actions shall be taken within the timeframes prescribed:
Any soil excavated from or treated at a release area during remediation shall be managed as follows:
Treatment, storage, disposal and transportation of soil which is hazardous waste, as defined pursuant to section 22a-448 of the Connecticut General Statutes, shall be carried out in conformance with the provisions of sections 22a-449(c)-101 to 119, inclusive, of the Regulations of Connecticut State Agencies, and any other applicable law;
In accordance with section 22a-209-8 of the Regulations of Connecticut State Agencies, the commissioner may authorize polluted soil, which is not hazardous waste, as defined in section 22a-448 of the Connecticut General Statutes, to be disposed of as special wastes, as defined in section 22a-209-1 of the Regulations of Connecticut State Agencies.
To be reused in any manner, polluted soil shall comply with all requirements of the RSRs, shall not be placed below the water table, shall not be placed in an area subject to erosion, and shall comply with the requirements in subparagraph (A), (B) or (C) of this subdivision. Prior to the reuse of such soil, a notice or request for the reuse of such soil pursuant to subparagraph (A), (B) or (C) of this subdivision shall be submitted to the commissioner in accordance with section 22a-133k-l(g) of the RSRs. Any such notice or request shall also include a map showing the proposed location and depth of the placement of such soil, and shall also demonstrate compliance with subparagraph (A), (B), or (C) of this subdivision. The commissioner may approve or deny in writing any request submitted pursuant to subparagraph (B) or (C) of this subdivision. No request shall be approved unless such request demonstrates to the commissioner's satisfaction, compliance with the requirements of subparagraph (B) or (C) of this subdivision, as applicable, and that the proposed reuse of soil is protective of human health and the environment.
Polluted soil may be used at any parcel of land if :
Notwithstanding the provisions of subdivision (3) of this subsection, the commissioner may approve or deny in writing a request for agricultural reuse of soil containing pesticides excavated on one parcel for reuse on another parcel. Any request regarding the reuse of soil under this subdivision shall be made to the commissioner in accordance with section 22a-133k-1(g) of the RSRs and, if soil is being reused on a parcel different from the parcel from which it was excavated, shall include the acknowledgement and consent of the owner of the parcel receiving such soil. No reuse shall be approved under this subdivision unless the request for reuse demonstrates to the commissioner's satisfaction that:
Nothing in the RSRs shall preclude the commissioner from taking any action necessary to prevent or abate pollution or to prevent or abate any threat to human health or the environment, including without limitation:
At any location at which, despite remediation in accordance with the RSRs, the commissioner determines that there is a potential ecological risk , the commissioner may require that an ecological risk assessment be conducted and that additional remediation be conducted to mitigate any risks identified in such assessment;
At any location at which polluted soil has eroded into a surface water body, the commissioner may require that the effect of such polluted soil on aquatic life be assessed and that remediation to protect or restore aquatic life and surface water quality from the effects of such polluted soil be undertaken; or
At any location at which there is polluted soil containing multiple polluting substances, the commissioner may require additional remediation to ensure that the risk posed by such substances does not exceed:
Conn. Agencies Regs. § 22a-133k-2