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. Author manuscript; available in PMC: 2015 Jul 31.
Published in final edited form as: Crit Rev Toxicol. 2015 Jan;45(1):1–43. doi: 10.3109/10408444.2014.973934

Table 3.

Summary of the animal studies used to derive PODs for each of the toxicities reviewed in RA1.

Toxic effect Oral exposure duration (vehicle) Species NOAEL/LOAEL (mg/kg bw per day) Calculated BMD/BMDL# (mg/kg bw per day) Reference
Reproductive toxicity Subchronic (corn oil) Male rat NA/1 No dose–response Zheng et al. (2010)
Neuro-developmental toxicity Acute (peanut oil) Male & female rat 0.02/0.2 0.09/0.05 (0.02) Chen et al. (2012)
Hepatotoxicity Subchronic (soybean oil) Male & female rat NA/3 No dose–response Wester et al. (2012)
Renal toxicity Subchronic (peanut oil) Male rat 5/50 Data not available Knuckles et al. (2001)
Cardiovascular toxicity Chronic (olive oil) Male mouse NA/2.5 No dose–response Yang et al. (2009)
Immunotoxicity Subchronic (soybean oil) Male rat 3/10 14/8.9 (4.8) De Jong et al. (1999)
Liver mutations Subchronic (olive oil) Male mouse NA/25 2.2/1.4 Lemieux et al. (2011)
Lung mutations Subchronic (olive oil) Male mouse NA/25 7.2/4.8 Lemieux et al. (2011)
Forestomach mutations Subchronic (olive oil) Male mouse NA/25 0.5/0.3 Lemieux et al. (2011)
Liver tumors Chronic (soybean oil) Male & female rat *2.1/7.1 *3.3/2.4 (1.2) Wester et al. (2012)
Forestomach tumors Chronic (soybean oil) Male & female rat *NA/2.1 *1.5/0.8 (1.1) Wester et al. (2012)
Forestomach tumors Chronic (diet) Female mouse 0/0.65 0.8/0.5 Culp et al. (1998)
*

Dose adjustment for time (dose × 5/7 dosing days) before modeling.

For comparison of rat and mouse BMDLs, scaled from rat to mouse by multiplying rat values by (0.03/0.35)¼ based on the assumption that the physiological processes scale with body weight to the ¾ power (allometric scaling).

#

Benchmark response: BMD10/BMDL10 for quantal data (tumor) and BMD1SD/BMDL1SD continuous data (Neurotoxicity, immunotoxicity and genotoxicity). Refer to supplemental table 4 for BMD model fit data.

NA, not available