Current through Register Vol. 41, No. 3, September 23, 2024
A. The
participant, with the concurrence of the department, shall consider impacts to
human health and the environment in establishing remediation levels.
B. Remediation levels based on human health
shall be developed after appropriate site characterization data have been
gathered as provided in
9VAC20-160-70. Remediation levels
may be derived from the three-tiered approach provided in this subsection. Any
tier or combination of tiers may be applied to establish remediation levels for
contaminants present at a given site.
1. Tier
I remediation levels are based on media backgrounds levels. These background
levels shall be determined from a portion of the property or a nearby property
or other areas as approved by the department that have not been impacted by the
contaminants of concern.
2. Tier II
remediation levels are derived assuming that there will be no restrictions on
the use of groundwater, surface water, and soil on the site.
a. Tier II groundwater remediation levels
shall be based on the most beneficial use of groundwater. The most beneficial
use of groundwater is for a potable water source, unless demonstrated otherwise
by the participant and accepted by the department. Therefore, they shall be
based on (i) federal Maximum Contaminant Levels (MCLs) or action levels for
lead and copper as established by the Safe Drinking Water Act (
42 USC §
300(f)) and the National
Primary Drinking Water Regulations ( 40 CFR Part 141) or, in the absence of a
MCL, (ii) tap water values derived using the methodology provided in the
Regional Screening Level Table, Region III, VI, and IX, United States
Environmental Protection Agency, December 2009, using an acceptable individual
carcinogenic risk of 1 X 10-5 and an individual
noncarcinogen hazard quotient of 0.1.
b. Tier II soil remediation levels shall be
determined as the lower of the ingestion or cross-media transfer values,
according to the following:
(1) For ingestion,
values derived using the methodology provided in the Regional Screening Level
Table, Region III, VI, and IX, United States Environmental Protection Agency,
December 2009.
(a) For carcinogens, the soil
ingestion concentration for each contaminant, reflecting an individual
upper-bound lifetime cancer risk of 1 X
10-5.
(b) For noncarcinogens, 0.1 of the soil
ingestion concentration, to account for multiple systemic toxicants at the
site. For sites where there are fewer than 10 contaminants exceeding 0.1 of the
soil ingestion concentration, the soil ingestion concentration may be divided
by the number of contaminants such that the resulting hazard index does not
exceed 1.0.
(2) For
cross-media transfer, values derived from the USEPA Soil Screening Guidance
(OSWER, July 1996, Document 9355.4-23, EPA/540/R-96/018) and USEPA Supplemental
Guidance for Developing Soil Screening Levels for Superfund Sites (OSWER,
December 2002, Document 9355.4-24) shall be used as follows:
(a) The soil screening level for transfer to
groundwater, with adjustment to a hazard quotient of 0.1 for noncarcinogens, if
the value is not based on a MCL; or
(b) The soil screening level for transfer to
air, with adjustment to a hazard quotient of 0.1 for noncarcinogens and a risk
level of 1 X 10-5 for carcinogens, using default
residential exposure assumptions.
(c) For noncarcinogens, for sites where there
are fewer than 10 contaminants exceeding 0.1 of the soil screening level, the
soil screening level may be divided by the number of contaminants such that the
resulting hazard index does not exceed 1.0.
(3) Values derived under subdivisions 2 b (1)
and (2) of this subsection may be adjusted to allow for updates in approved
toxicity factors as necessary.
c. Tier II remediation levels for surface
water shall be based on the Virginia Water Quality Standards (WQS) as
established by the State Water Control Board (9VAC25-260), according to the
following:
(1) The chronic aquatic life
criteria shall be compared to the appropriate human health criteria and the
lower of the two values selected as the Tier II remediation level.
(2) For contaminants that do not have a
Virginia WQS, the federal Water Quality Criteria (WQC) may be used if
available. The chronic federal criterion continuous concentration (CCC) for
aquatic life shall be compared to the appropriate human health based criteria
and the lower of the two values selected as the Tier II remediation
level.
(3) If neither a Virginia
WQS nor a federal WQC is available for a particular contaminant detected in
surface water, the participant should perform a literature search to determine
if alternative values are available. If alternative values are not available,
the detected contaminants shall be evaluated through a site-specific risk
assessment.
3. Tier III remediation levels are based upon
site-specific assumptions about current and potential exposure scenarios for
the population or populations of concern and characteristics of the affected
media and can be based upon a site-specific risk assessment. Land-use controls
can be considered.
a. In developing Tier III
remediation levels, and unless the participant proposes other guidance that is
acceptable to the department, the participant shall use, for all media and
exposure routes, the methodology specified in Risk Assessment Guidance for
Superfund, Volume 1, Human Health Evaluation Manual (Part A), Interim Final,
USEPA, December 1989 (EPA/540/1-89/002) and (Part B, Development of Preliminary
Remediation Goals) Interim, USEPA, December 1991 (Publication 9285.7-01B) with
modifications as appropriate to allow for site-specific conditions. The
participant may use other methodologies approved by the department.
b. For a site with carcinogenic contaminants,
the remediation goal for individual carcinogenic contaminants shall be an
incremental upper-bound lifetime cancer risk of 1 X
10-5. The remediation levels for the site shall not
result in an incremental upper-bound lifetime cancer risk exceeding 1 X
10-4 considering multiple contaminants and multiple
exposure pathways, unless the use of a MCL for groundwater that has been
promulgated under 42 USC
§
300g-1 of the Safe Drinking Water Act
and the National Primary Drinking Water Regulations ( 40 CFR Part 141) results
in a cumulative risk greater than 1 X
10-4.
c.
For noncarcinogens, the hazard index shall not exceed a combined value of
1.0.
d. In setting remediation
levels, the department may consider risk assessment methodologies approved by
another regulatory agency and current at the time of the Voluntary Remediation
Program site characterization.
C. The participant shall determine if
ecological receptors are present at the site or in the vicinity of the site and
if they are impacted by releases from the site.
1. At sites where ecological receptors are of
concern and there are complete exposure pathways, the participant shall perform
a screening level ecological evaluation demonstrating that remediation levels
developed under the three-tiered approach described in this section are also
protective of such ecological receptors.
2. For sites where a screening level
ecological evaluation has shown that there is a potential for ecological risks,
the participant shall perform an ecological risk assessment demonstrating that
remediation levels developed under the three-tiered approach described in this
section are also protective of ecological receptors. If the remediation levels
developed for human health are not protective of ecological receptors, the
remediation levels shall be adjusted accordingly.
Statutory Authority: §
10.1-1232 of the Code of
Virginia.