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propylamine in drinking water at 0.9 mg/day for 5 days/week for 30 weeks resulting in a daily dose of<br />

2.6 mg/kg-day. No control group was included. Esophageal carcinomas (20/20) and forestomach<br />

tumors (12/20) developed in exposed animals.<br />

IV.<br />

DERIVATION OF CANCER POTENCY<br />

Basis for Cancer Potency<br />

US EPA (1986) based its selection of a cancer potency on a study which demonstrates induction of<br />

liver tumors by N-nitrosodi-n-propylamine. US EPA (1986) used the data from Druckrey et al.(1967)<br />

in the induction of hepatocellular carcinoma in BD rats exposed to N-nitrosodi-n-propylamine in<br />

drinking water to calculate a cancer potency value.<br />

Methodology<br />

The high tumor incidence in all the N-nitrosodi-n-propylamine treated animals suggests time-dependent<br />

analysis is more appropriate than multistage analysis in the derivation of a cancer potency value. A<br />

dosage estimate for use in deriving the cancer potency value was based on the following relationship,<br />

where d is the daily dose, C is the mmol to mg conversion factor (130.2 mg/mmol), k is an empirically<br />

derived constant estimated from a plot of k versus the number of carbon atoms for lower di-Nalkylnitrosamines<br />

(k=1.7 × 10 4 mmol/kg-day), t 50 is the median time of tumor induction, and n is a<br />

representative value for dialkylnitrosamines (n=2.3; Druckrey et al., 1967):<br />

d = C × k<br />

The resulting daily dose estimate was 0.578 mg/kg-day. Applying this estimate to a rearrangement of<br />

the one-hit model gave an animal cancer potency value (q animal ) of 1.2 (mg/kg-day) -1 .<br />

q animal = -ln(0.5/day) / d<br />

Conversion of the q animal to a human cancer potency estimate (q human ) was made based on the following<br />

relationship, where bw h is the assumed human body weight (70 kg) and bw a is the assumed<br />

experimental animal body weight (0.35 kg):<br />

t 50<br />

n<br />

q human = q animal × (bw h /bw a ) 1/3<br />

The resulting estimate of q human was 7.0 (mg/kg-day) -1 .<br />

A unit risk value based upon air concentrations was derived by <strong>OEHHA</strong>/ATES using an assumed<br />

human breathing rate of 20 m 3 /day, 70 kg human body weight, and 100% fractional absorption after<br />

inhalation exposure. The calculated unit risk value is 2.0 E-3 (µg/m 3 ) -1 .<br />

394

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