35 Ill. Adm. Code 742.715
RBCA Soil Equations
Section 742
Section 742.715Â RBCA Soil
Equations
a)Â Â Â Â Â Â Â Â This Section presents the RBCA model and describes the
equations and parameters used to develop Tier 2 soil remediation objectives.
b)Â Â Â Â Â Â Â Â Ingestion, Outdoor Inhalation, and Dermal Contact
1)Â Â Â Â Â Â Â Â The two sets of equations in subsections (b)(2) and (b)(3) shall
be used to generate Tier 2 soil remediation objectives for the combined
ingestion, outdoor inhalation, and dermal contact with soil exposure routes.
2)Â Â Â Â Â Â Â Â Combined Exposure Routes of Soil Ingestion, Outdoor Inhalation
of Vapors and Particulates, and Dermal Contact with Soil
A)Â Â Â Â Â Â Â Equations R1 and R2 form the basis for deriving Tier 2
remediation objectives for the set of equations that evaluates the combined
exposure routes of soil ingestion, outdoor inhalation of vapors and
particulates, and dermal contact with soil using the RBCA approach. Equation
R1 is used to calculate soil remediation objectives for carcinogenic
contaminants. Equation R2 is used to calculate soil remediation objectives for
noncarcinogenic contaminants. Soil remediation objectives for the outdoor
inhalation exposure route from subsurface soils must also be calculated in
accordance with the procedures outlined in subsection (b)(3) of this Section
and compared to the values generated from Equations R1 or R2. The smaller
value (i.e., R1 and R2 compared to R7 and R8, respectively) from these
calculations is the Tier 2 soil remediation objective for the combined exposure
routes of soil ingestion, outdoor inhalation, and dermal contact with soil.
B)Â Â Â Â Â Â Â In Equation R1, numerical values are calculated for two
parameters:
i)Â Â Â Â Â Â Â Â Â The volatilization factor for surficial soils (VF
ss
)
using Equations R3 and R4; and
ii)Â Â Â Â Â Â Â Â The volatilization factor for surficial soils regarding
particulates (VF
p
) using Equation R5.
C)Â Â Â Â Â Â Â VF
ss
uses Equations R3 and R4 to derive a numerical
value. Equation R3 requires the use of Equation R6. Both equations must be
used to calculate the VF
ss
. The lowest calculated value from these
equations must be substituted into Equation R1.
D)Â Â Â Â Â Â Â The remaining parameters in Equation R1 have either default
values listed in Appendix C, Table D or toxicological-specific information
(i.e., SF
o
, SF
i
), which can be obtained by following the
guidelines in OSWER Directive 9285.7-53, as incorporated by reference in Section
742.210 or requested from the program under which the remediation is being
performed.
E)Â Â Â Â Â Â Â For Equation R2, the parameters VF
ss
and VF
p
are calculated. The remaining parameters in Equation R2 have either default
values listed in Appendix C, Table D or toxicological-specific information
(i.e., RfD
o
,
RfD
i
), which can be obtained by
following the guidelines in OSWER Directive 9285.7-53, as incorporated by
reference in Section 742.210 or requested from the program under which the
remediation is being performed.
F)Â Â Â Â Â Â Â Â For chemicals other than inorganics which do not have default
values for the dermal absorption factor (RAF
d
) in Appendix C, Table
D a dermal absorption factor of 0.5 shall be used for Equations R1 and R2. For
inorganics, dermal absorption may be disregarded (i.e., RAF
d
= 0).
3)Â Â Â Â Â Â Â Â Outdoor Inhalation Exposure Route from Subsurface Soils (soil
below one meter)
A)Â Â Â Â Â Â Â Equations R7 and R8 form the basis for deriving Tier 2
remediation objectives for the outdoor inhalation exposure route from subsurface
soils using the RBCA approach. Equation R7 is used to calculate soil
remediation objectives for carcinogenic contaminants. Equation R8 is used to
calculate soil remediation objectives for noncarcinogenic contaminants.
B)Â Â Â Â Â Â Â For Equation R7, the carcinogenic risk-based screening level
for air (RBSL
air
) and the volatilization factor for soils below one meter
to ambient air (VF
samb
) have numerical values that are calculated using
Equations R9 and R11, respectively. Both equations rely on input parameters from
a variety of sources.
C)Â Â Â Â Â Â Â The noncarcinogenic risk-based screening level for air (RBSL
air
)
and the volatilization factor for soils below one meter to ambient air (VF
samb
)
in Equation R8 have numerical values that can be calculated using Equations R10
and R11, respectively.
c)Â Â Â Â Â Â Â Â Soil Component of the Groundwater Ingestion Exposure Route
1)Â Â Â Â Â Â Â Â Equation R12 forms the basis for deriving Tier 2 remediation
objectives for the soil component of the groundwater ingestion exposure route
using the RBCA approach. The parameters, groundwater at the source (GW
source
)
and Leaching Factor (LF
sw
), have numerical values that are
calculated
using Equations R13 and R14, respectively.
2)Â Â Â Â Â Â Â Â Equation R13 requires numerical values that are calculated
using Equation R15.
3)Â Â Â Â Â Â Â Â Equation R14 requires numerical values that are calculated
using Equations R21, R22, and R24. For non-ionizing organics, the Soil Water
Sorption Coefficient (k
s
) shall be calculated using Equation R20. Â For
ionizing organics and inorganics, the values for k
s
are listed in
Appendix C, Tables I and J, respectively. The pH-dependent k
s
values
for ionizing organics can be calculated using Equation R20 and the pH dependent
K
oc
values in Appendix C, Table I. The remaining parameters
in Equation R14 are field measurements or default values listed in Appendix C,
Table D.
d)Â Â Â Â Â Â Â Â The default value for GW
comp
is the Tier 1
groundwater remediation objective. For chemicals for which there is no Tier 1
groundwater remediation objective, the value for GW
comp
shall be the
concentration determined according to the procedures specified in 35 Ill. Adm.
Code 620, Subpart F. As an alternative to using the above concentrations, GW
comp
may be developed using Equations R25 and R26, if approved institutional
controls are in place as may be required in Subpart J.