Appendix D - Model Input Parameters for BAF-QSAR and Terrestrial Biomagnification Model Predictions for decaBDE Transformation Products
Metabolite | Log Kow | Median kM (1/d) (184 g fish at 15°C |
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[1] Estimated using KOWWIN. [2] Lowest QSAR estimates from the supporting working document (Environment Canada 2006b). [3] Maximum measured value (Watanabe and Tatsukawa 1990). [4] kM based on Tomy et al. (2004) and normalized to weight of middle trophic level fish in Arnot and Gobas (2004) model and 15°C. These metabolites are expected to undergo further metabolism; however, the actual rates of metabolism are unknown. [5] Information regarding the half-life and kM of nonaBDEs is lacking in the literature and a half-life of 26 d (equal to that of decaBDE) was therefore assumed. Normalized to weight of middle trophic level fish in Arnot and Gobas (2004) model and 15°C. [6] Based on a half-life of 19 d (Tomy et al. 2004) and normalized to weight of middle trophic level fish in Arnot and Gobas model and 15°C. [7] Based on a half-life of 38 d (Stapleton et al. 2004, Tomy et al. 2004 -- estimates ranged from 19 to 346 d) and normalized to weight of middle trophic level fish in Arnot and Gobas (2004) model and 15°C. [8] Based on a half-life of 58 d (Stapleton et al. 2004, Tomy et al. 2004 -- estimates ranged from 23 to 231 d) and normalized to weight of middle trophic level fish in Arnot and Gobas (2004) model and 15°C. [9] Based on half-life of 50.7 d (Stapleton et al. 2004, Tomy et al. 2004 -- estimates ranged from 43 to 173 d) and normalized to weight of middle trophic level fish in Arnot and Gobas (2004) model and 15°C. |
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Hydroxymethoxy-octaBDEs | 8.78 [1] | 0.02 [4] |
Hydroxymethoxy-hexaBDEs | 7.89 [1] | 0.02 [4] |
Hydroxymethoxy-pentaBDEs | 7 [1] | 0.02 [4] |
Hydroxymethoxy-heptaBDEs | 8.78 [1] | 0.02 [4] |
Hydroxy-hexaBDEs | 8.07 [1] | 0.02 [4] |
Hydroxy octaBDEs | 10.4 [1] | 0.02 [4] |
Hydroxy-nonaBDEs | 10.74 [1] | 0.02 [4] |
nonaBDEs | 10.1 [2] | 0.02 [5] |
octaBDEs | 8.9 [3] | 0.03 [6] |
heptaBDEs | 8.79 [2] | 0.01 [7] |
hexaBDEs | 7.9 [3] | 0.001 [8] |
pentaBDEs | 7 [3] | 0.001 [9] |
Name and Structure | Log Kow | Log Koa | ED [9] | kM (1/d) (wolf body weight normalized 80 kg |
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[1] Estimated using KOWWIN. [2] Estimated using KOWWIN. [3] Lowest QSAR estimates from the supporting working document. [4] Maximum measured value (Watanabe and Tatsukawa 1990). [5] Average based on longest observed half-lives for decaBDE, nonaBDEs and octaBDEs by Huwe and Smith (2007a, b) and normalized to body weight of wolf in Gobas model (80 kg). [6] Based on longest half-life of 22.6 d for nonaBDEs observed by Huwe and Smith (2007a, b) and normalized to body weight of wolf in Gobas model (80 kg). [7] Based on longest half-life of 64.8 d for octaBDEs observed by Huwe and Smith (2007a, b) and normalized to body weight of wolf in Gobas model (80 kg). [8] Based on half-life of 43.7 d (average of half-lives for nona- and octaBDEs) and normalized to body weight of wolf in Gobas model (80 kg). [9] Estimated according to Kelly et al. (2004; and personal communication from BC Kelly to Mark Bonnell, Environment Canada, January 2008; unreferenced) based on ED for dairy cows. |
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Hydroxymethoxy octaBDE | 8.78 [1] | 19.1 [2] | 5% | 0.004 [5] |
Hydroxymethoxy pentaBDE | 7 [1] | 16.53 [2] | 67% | 0.004 [5] |
Hydroxymethoxy hexaBDE | 7.9 [1] | 17.8 [2] | 29% | 0.004 [5] |
Hydroxymethoxy heptaBDE | 8.8 [1] | 19.1 [2] | 5% | 0.004 [5] |
Hydroxy-hexaBDE | 8.1 [1] | 16.8 [2] | 20% | 0.004 [5] |
hydroxy-octaBDE, | 10.4 [1] | 19.4 [2] | 1% | 0.004 [5] |
hydroxy-nonaBDE | 10.7 [1] | 20.6 [2] | 1% | 0.004 [5] |
nonaBDEs | 10.1 [3] | 17.13 [2] | 1% | 0.007 [6] |
octaBDEs | 8.9 [4] | 15.85 [2] | 4% | 0.003 [7] |
heptaBDEs | 8.8 [3] | 14.55 [2] | 5% | 0.004 [8] |
hexaBDEs | 8.23 [3] | 13.265 | 17% | 0.004 [8] |
Product | Smiles | Log Kow [1] | Log Koa [2] | Aquatic kM [3] (1/d) | Mammal kM [4] (1/d) | ED |
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[1] Estimated using KOWWIN. [2] Estimated using KOWWIN. [3] kM for these metabolites is illustrative only and is consistent with a half-life of 26 d and normalized to weight of middle trophic level fish in Arnot and Gobas (2004) model and15°C. These metabolites are expected to undergo further metabolism; however, the actual rates of metabolism are unknown. [4] Average based on longest observed half-lives for decaBDE, nonaBDEs and octaBDEs by Huwe and Smith (2007a, b) and normalized to body weight of wolf in Gobas model (80 kg); kM for these metabolites is illustrative only and is consistent with a half-life of 26 d. These metabolites are expected to undergo further metabolism; however, the actual rates of metabolism are unknown. |
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triBDFs | C12=CC(Br)=C(Br)C=C1OC3=C2C=C(Br)C=C3 | 6.72 | 10.639 | 0.02 | 0.004 | 74% |
tetraBDFs | C12=CC(Br)=C(Br)C=C1OC3=C2C=C(Br)C(Br)=C3 | 7.61 | 11.99 | 0.02 | 0.004 | 42% |
pentaBDFs | C12=CC(Br)=C(Br)C=C1OC3=C2C=C(Br)C(Br)=C3Br | 8.5 | 13.27 | 0.02 | 0.004 | 10% |
hexaBDFs | C12=C(Br)C(Br)=C(Br)C=C1OC3=C2C=C(Br)C(Br)=C3Br | 9.39 | 14.56 | 0.02 | 0.004 | 1% |
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