(1) General
considerations.
(a) This section applies
whenever it is necessary to establish air cleanup standards to determine if air
emissions at a site pose a threat to human health or the environment. It
applies to ambient (outdoor) air and air within any building, utility vault,
manhole or other structure large enough for a person to fit into. This section
does not apply to concentrations of hazardous substances in the air originating
from an industrial or commercial process or operation or to hazardous
substances in the air originating from an offsite source. This section does
apply to concentrations of hazardous substances in the air originating from
other contaminated media or a remedial action at the site. Air cleanup
standards shall be established at the following sites:
(i) Where a nonpotable groundwater cleanup
level is being established for volatile organic compounds using a site-specific
risk assessment under WAC
173-340-720(6).
(ii) Where a soil cleanup level that
addresses vapors or dust is being established under WAC
173-340-740 or
173-340-745.
(iii) Where it is necessary to establish air
emission limits for a remedial action.
(iv) At other sites as determined by the
department.
(b) Cleanup
levels to protect air quality shall be based on estimates of the reasonable
maximum exposure expected to occur under both current and future site use
conditions. The department has determined that residential site use will
generally require the most protective air cleanup levels and that exposure to
hazardous substances under these conditions represents the reasonable maximum
exposure. Air cleanup levels shall use this presumed exposure scenario and be
established in accordance with subsection (3) of this section unless the site
qualifies for a Method C air cleanup level. If a site qualifies for a Method C
air cleanup level, subsection (4) of this section shall be used to establish
air cleanup levels.
(c) In the
event of a release or potential release of hazardous substances into the air at
a site at which this section applies under (a) of this subsection, a cleanup
action that complies with this chapter shall be conducted to address all areas
of the site where the concentration of the hazardous substances in the air
exceeds cleanup levels.
(d) Air
cleanup levels shall be established at concentrations that do not directly or
indirectly cause violations of groundwater, surface water, or soil cleanup
standards established under this chapter or applicable state and federal laws.
A site that qualifies for a Method C air cleanup level under this section does
not necessarily qualify for a Method C cleanup level in other media. Each
medium must be evaluated separately using the criteria applicable to that
medium.
(e) The department may
require more stringent air cleanup standards than required by this section
where, based on a site-specific evaluation, the department determines that this
is necessary to protect human health and the environment. Any imposition of
more stringent requirements under this provision shall comply with WAC
173-340-702 and
173-340-708.
(2) Method A air cleanup levels.
This section does not provide procedures for establishing
Method A cleanup levels. Method B or C, as appropriate, shall be used to
establish air cleanup levels.
(3) Method B air cleanup levels.
(a) Applicability. Method B air cleanup
levels consist of standard and modified cleanup levels as described in this
subsection. Either standard or modified Method B air cleanup levels may be used
at any site.
(b) Standard Method B
air cleanup levels. Standard Method B cleanup levels for air shall be at least
as stringent as all of the following:
(i)
Applicable state and federal laws. Concentrations established under applicable
state and federal laws; and
(ii)
Human health protection. For hazardous substances for which sufficiently
protective health-based criteria or standards have not been established under
applicable state and federal laws, those concentrations which protect human
health and the environment as determined by the following methods:
(A) Noncarcinogens. Concentrations that are
estimated to result in no acute or chronic toxic effects on human health and
are determined using the following equation and standard exposure assumptions:
[Equation 750-1]
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(B)
Carcinogens. For known or suspected carcinogens, concentrations for which the
upper bound on the estimated excess cancer risk is less than or equal to one in
1,000,000 (1 x 10
-6) and are determined using the
following equation standard exposure assumptions:
[Equation 750-2]
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(C)
Petroleum mixtures. For noncarcinogenic effects of petroleum mixtures, a total
petroleum hydrocarbon cleanup level shall be calculated using Equation 750-1
and by taking into account the additive effects of the petroleum fractions and
volatile organic compounds present in the petroleum mixture. Cleanup levels for
other noncarcinogens and known or suspected carcinogens within the petroleum
mixture shall be calculated using Equations 750-1 and 750-2. See Table 830-1
for the analyses required for various petroleum products to use this
method.
(iii) Lower
explosive limit limitation. Standard Method B air cleanup levels shall not
exceed 10 percent of the lower explosive limit for any hazardous substance or
mixture of hazardous substances.
(c) Modified Method B air cleanup levels.
Modified Method B air cleanup levels are standard Method B air cleanup levels
modified with chemical-specific or site-specific data. When making these
adjustments, the resultant cleanup levels shall meet applicable state and
federal laws, health risk levels and explosive limit limitations required for
standard Method B air cleanup levels. Changes to exposure assumptions must
comply with WAC
173-340-708(10).
The following adjustments may be made to the default assumptions in the
standard Method B equations to derive modified Method B cleanup levels:
(i) The inhalation absorption fraction may be
modified if the requirements of WAC
173-340-702(14), (15),
(16) and WAC
173-340-708(10)
are met;
(ii) Adjustments to the
reference dose and cancer potency factor may be made if the requirements in WAC
173-340-708(7) and
(8) are met;
(iii) The toxicity equivalency factor
procedures described in WAC
173-340-708(8)
may be used for assessing the potential carcinogenic risk of mixtures of
chlorinated dibenzo-p-dioxins, chlorinated diben-zofurans and polycyclic
aromatic hydrocarbons;
(iv)
Modifications incorporating new science as provided for in WAC
173-340-702(14), (15) and
(16); and
(d) Using modified Method B to evaluate air
remediation levels. In addition to the adjustments allowed under subsection
(3)(c) of this section, adjustments to the reasonable maximum exposure scenario
or default exposure assumptions are allowed when using a quantitative
site-specific risk assessment to evaluate the protectiveness of a remedy. See
WAC
173-340-355,
173-340-357 and
173-340-708(3)(d) and
(10)(b).
(4) Method C air cleanup levels.
(a) Applicability. Method C air cleanup
levels consist of standard and modified cleanup levels as described in this
subsection. Method C air cleanup levels may be approved by the department if
the person undertaking the cleanup action can demonstrate that the site
qualifies for use of Method C under WAC
173-340-706(1).
(b) Standard Method C air cleanup levels.
Standard Method C air cleanup levels for ambient air shall be at least as
stringent as all of the following:
(i)
Applicable state and federal laws. Concentrations established under applicable
state and federal laws;
(ii) Human
health protection. For hazardous substances for which sufficiently protective
health-based criteria or standards have not been established under applicable
state and federal laws, concentrations that protect human health and the
environment as determined by the following methods:
(A) Noncarcinogens. Concentrations that are
anticipated to result in no significant acute or chronic effects on human
health and are estimated in accordance with Equation 750-1 except that the
average body weight shall be 70 kg and the estimated breathing rate shall be 20
m3/day;
(B) Carcinogens. For known or suspected
carcinogens, concentrations for which the upper bound on the estimated excess
cancer risk is less than or equal to one in 100,000 (1 x
10-5) and are determined in accordance with Equation
750-2.
(C) Petroleum mixtures.
Cleanup levels for petroleum mixtures shall be calculated as specified in
subsection (3)(b)(ii)(C) of this section, except that the average body weight
shall be 70 kg and the estimated breathing rate shall be
20m3/day.
(iii) Lower explosive limit limitation.
Standard Method C air cleanup levels shall not exceed 10 percent of the lower
explosive limit for any hazardous substance or mixture of hazardous
substances.
(c) Modified
Method C air cleanup levels. Modified Method C air cleanup levels are standard
Method C air cleanup levels modified with chemical-specific or site-specific
data. The same limitations and adjustments specified in subsection (3)(c) of
this section apply to modified Method C cleanup levels.
(d) Using modified Method C to evaluate air
remediation levels. In addition to the adjustments allowed under subsection
(4)(c) of this section, adjustments to the reasonable maximum exposure scenario
or default exposure assumptions are allowed when using a quantitative
site-specific risk assessment to evaluate the protectiveness of a remedy. See
WAC
173-340-355,
173-340-357 and
173-340-708(3)(d) and
(10)(b).
(5) Adjustments to air cleanup levels.
(a) Total site risk adjustments. Air cleanup
levels for individual hazardous substances developed in accordance with
subsections (3) and (4) of this section, including cleanup levels based on
applicable state and federal laws, shall be adjusted downward to take into
account exposure to multiple hazardous substances and/or exposure resulting
from more than one pathway of exposure. These adjustments need to be made only
if, without these adjustments, the hazard index would exceed one or the total
excess cancer risk would exceed one in 100,000 (1 x
10
-5). These adjustments shall be made in accordance
with the procedures in WAC
173-340-708(5) and
(6). In making these adjustments, the hazard
index shall not exceed one and the total excess cancer risk shall not exceed
one in 100,000 (1 x 10
-5).
(b) Adjustments to applicable state and
federal laws. Where a cleanup level developed under subsection (3) or (4) of
this section is based on an applicable state or federal law and the level of
risk upon which the standard is based exceeds an excess cancer risk of one in
100,000 (1 x 10-5) or a hazard index of one, the
cleanup level must be adjusted downward so that the total excess cancer risk
does not exceed one in 100,000 (1 x 10-5) and the
hazard index does not exceed one at the site.
(c) Natural background and PQL
considerations. Cleanup levels determined under subsection (3) or (4) of this
section, including cleanup levels adjusted under (a) or (b) of this subsection,
shall not be set at levels below the practical quantitation limit or natural
background, whichever is higher. See WAC
173-340-709 and
173-340-707 for additional
requirements pertaining to practical quantitation limits and natural
background.
(6) Points of
compliance. Cleanup levels established under this section shall be attained in
the ambient (outdoor) air and air within any building, utility vault, manhole
or other structure large enough for a person to fit into, throughout the site.
For sites determined to be industrial sites under the criteria in WAC
173-340-745, the department may
approve a conditional point of compliance not to exceed the property boundary.
A conditional point of compliance shall not be approved if use of a conditional
point of compliance would pose a threat to human health or the
environment.
(7) Compliance
monitoring.
(a) Where air cleanup levels have
been established at a site, monitoring may be required to be conducted to
determine if compliance with the air cleanup levels has been achieved. Sampling
and analytical procedures shall be defined in a compliance monitoring plan
prepared under WAC
173-340-410. The sample design
shall provide data that are representative of the site.
(b) Data analysis and evaluation procedures
used to evaluate compliance with air cleanup levels shall be defined in a
compliance monitoring plan prepared under WAC
173-340-410.
(c) Averaging times specified in applicable
state and federal laws shall be used to demonstrate compliance with those
requirements.
(d) When cleanup
levels are not based on applicable state and federal laws, the following
averaging times shall be used:
(i) Compliance
with air cleanup levels for noncarcinogens shall be based on 24-hour time
weighted averages except where the cleanup level is based upon an inhalation
reference dose which specifies an alternate averaging time;
(ii) Compliance with air cleanup levels for
carcinogens shall be based on annual average
concentrations.