Compound | GothiaTek limit (ng/g dry weight) | Laboratory‡ method detection limit (ng/g dry weight) | Compound TD50 (mg/kg body weight/day) | Cancer potency factor ((mg/kg body weight/day)−1) | Cancer risk estimate (100% transfer) | Cancer risk estimate (reduced percentage transfer) | |
TSNA* | 10000 | 230§ | 0.0999 | 10.1 | 6.2×10E−3 | 5.3×10E−3 | |
BaP (BaPeq)† | 20 (40)† | 0.04 | 0.956 | 1.1 | 2.7×10E−6 | 1.6×10E−7 | |
Cadmium | 1000 | 43.3 | 0.0217 | 46.1 | 2.8×10E−3 | 1.7×10E−4 | |
Lead | 2000 | 37.9 | 46.6 | 0.02 | 2.5×10E−6 | 1.5×10E−7 | |
Arsenic | 500 | 25 | No comparable CPDB data | ||||
Chromium | 3000 | 11.9 | No comparable CPDB data | ||||
Product total risk | 9.0×10E−3 | 8.1×10E−3 |
↵* TD50 (chronic dose rate in mg/kg body weight/day, which would induce tumours in half the test animals at the end of a standard lifespan for the species) for NNK and NNN was used as a conservative estimate of risk for the composite of TSNAs and 85% bioavailability was assumed for each when calculating reduced percentage transfer.24
↵† Cancer risk estimates were based on concentrations using BaP equivalents (BaPeq) to represent contributions from other carcinogenic PAHs.
↵‡ These are detection limits for the selected constituents in processed tobacco as reported by the laboratory that tested the STPs used in this study.
↵§ This was based on the analysis of the tobacco ‘as received’.
BaP, benzo(a)pyrene; CPDB, carcinogenic potency database; NNK, 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone; NNN, N'-nitrosonornicotine; PAH, polycyclic aromatic hydrocarbon; TSNA, tobacco specific nitrosamine.