[Equation 750-1] |
Air cleanup level (ug/m3) | = | RfD x ABW x UCF x HQ x AT |
BR x ABS x ED x EF |
Where: |
RfD | = | Reference dose as specified in WAC 173-340-708(7) (mg/kg-day) |
ABW | = | Average body weight over the exposure duration (16 kg) |
UCF | = | Unit conversion factor (1,000 ug/mg) |
BR | = | Breathing rate (10 m3/day) |
ABS | = | Inhalation absorption fraction (1.0) (unitless) |
HQ | = | Hazard quotient (1) (unitless) |
AT | = | Averaging time (6 years) |
ED | = | Exposure duration (6 years) |
EF | = | Exposure frequency (1.0) (unitless) |
(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 one million (1 x 10-6) and are determined using the following equation and standard exposure assumptions:
[Equation 750-2] |
Air cleanup level (ug/m3) | = | RISK x ABW x AT x UCF |
CPF x BR x ABS x ED x EF |
Where: |
RISK | = | Acceptable cancer risk level (1 in 1,000,000) (unitless) |
ABW | = | Average body weight over the exposure duration (70 kg) |
AT | = | Averaging time (75 years) |
UCF | = | Unit conversion factor (1,000 ug/mg) |
CPF | = | Carcinogenic potency factor as specified in WAC 173-340-708(8) (kg-day/mg) |
BR | = | Breathing rate (20 m3/day) |
ABS | = | Inhalation absorption fraction (1.0) (unitless) |
ED | = | Exposure duration (30 years) |
EF | = | Exposure frequency (1.0) (unitless) |
(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 ten percent (10%) 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 percentage 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 dibenzofurans 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 one hundred thousand (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 ten percent (10%) 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 (1) or the total excess cancer risk would exceed one in one hundred thousand (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 (1) and the total excess cancer risk shall not exceed one in one hundred thousand (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 one hundred thousand (1 x 10-5) or a hazard index of one (1), the cleanup level must be adjusted downward so that the total excess cancer risk does not exceed one in one hundred thousand (1 x 10-5) and the hazard index does not exceed one (1) 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 air 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 twenty-four-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.
[Statutory Authority: Chapter
70.105D RCW. WSR 01-05-024 (Order 97-09A), § 173-340-750, filed 2/12/01, effective 8/15/01; WSR 91-04-019, § 173-340-750, filed 1/28/91, effective 2/28/91.]
Reviser's note: The brackets and enclosed material in the text of the above section occurred in the copy filed by the agency.