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PRINCIPLES OF TOXICOLOGY

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19.4 PETROLEUM HYDROCARBONS: ASSESSING EXPOSURE AND RISK TO MIXTURES 485<br />

TABLE 19.2 Example—Worker Exposure to Diesel Fuel Hydrocarbons in Soil, Typical Reasonable<br />

Maximum Exposure Soil Exposure Parameters<br />

Exposure Parameter Value Reference<br />

ABSgi 1 Default<br />

ABSsk 0.05 Professional judgment<br />

AF 0.2 mg/cm 2<br />

USEPA (1997)<br />

ATnc 9125 days USEPA (1991)<br />

BW 70 kg USEPA (1991)<br />

ED 25 years USEPA (1991)<br />

EF 250 days/year USEPA (1991)<br />

IR 50 mg/day USEPA (1991)<br />

SA 2000 cm 2<br />

USEPA (1992)<br />

HQ or HI exceeds one, there may be a concern for adverse effects. Exposure assumptions used to<br />

calculate exposure to petroleum hydrocarbons in soil are presented in Table 19.2.<br />

The average daily intakes (ADIs) of the six petroleum hydrocarbon fractions are presented in Table<br />

19.3. These ADIs were calculated using the soil concentrations in Table 19.1, the exposure assumptions<br />

presented in Table 19.2, and the equations presented later in this chapter (see Table 19.10).<br />

HQs associated with the calculated levels of exposure to petroleum hydrocarbons in soil are<br />

calculated by dividing the calculated ingestion and dermal intake by RfD for the appropriate petroleum<br />

hydrocarbon fraction. The calculated HQs for the six petroleum hydrocarbon fractions are presented<br />

in Table 19.4.<br />

Several petroleum fractions may affect the same target organ or have similar critical effects. In the<br />

absence of strong evidence indicating another type of interaction (an antagonistic effect or a synergistic<br />

effect), the USEPA assumes that the effects of chemicals affecting the same target organ are additive.<br />

Thus, the hazard quotients for chemicals affecting the same target organ are summed. The sum of the<br />

HQs for a particular target organ is termed the HI. The calculated HIs for liver toxicity, decreased body<br />

weight, and kidney toxicity are presented below.<br />

HI for liver toxicity = sum of the oral and dermal HQs for aliphatic petroleum fractions C>12–C16,<br />

C>16–C21, and C>21–C35 = 0.024<br />

TABLE 19.3 Example—Worker Exposure to Diesel Fuel Hydrocarbons in Soil, Calculated Average<br />

Daily Intakes of Diesel Fuel Hydrocarbons<br />

Average Daily Intake<br />

Petroleum Hydrocarbon Fraction Ingestion (mg/kg) Dermal (mg/kg)<br />

C>12–C16<br />

C>16–C21<br />

C>21–C35<br />

C>12–C16<br />

C>16–C21<br />

C>21–C35<br />

Aliphatic<br />

1.08 × 10 –3<br />

8.81 × 10 –3<br />

3.23 × 10 –3<br />

Aromatic<br />

7.34 × 10 –4<br />

4.55 × 10 –3<br />

4.45 × 10 –3<br />

4.31 × 10 –4<br />

3.52 × 10 –3<br />

1.29 × 10 –3<br />

2.94 × 10 –4<br />

1.82 × 10 –3<br />

1.78 × 10 –3

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