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Appendices of Final Screening Assessment
Petroleum Sector Stream Approach
Heavy Fuel Oils
[Industry-Restricted]
Chemical Abstracts Service Registry Numbers
64741-75-9
68783-08-4
70592-76-6
70592-77-7
70592-78-8
Environment Canada
Health Canada
July 2013
Appendices
- Appendices 1 to 4
- Appendix 5: Modelling results for environmental properties of industryrestricted HFOs
- Table A5.1. Results of the Level III fugacity modelling (EQC 2003)
- Table A5.2. Modelled data for primary (BioHCWin 2008; BIOWIN4 2009) and ultimate (BIOWIN3, 5 and 6 2009; CATABOL; TOPKAT) degradation of HFO components
- Table A5.3. Potential presence of persistent representative structures
- Table A5.4. Proportion (weight %) of persistent representative structures in three samples of Fuel Oil No. 6 (Fuhr 2008)
- Table A5.5. Modelled atmospheric degradation of representative structures for HFOs via reaction with hydroxyl radicals (AOPWIN 2008)
- Table A5.6. Experimental BAFs for aromatic hydrocarbons
- Table A5.7. Summary of empirical aquatic bioconcentration factors (BCFs) for various PAHs (adapted from European Commission 2008b)
- Tables A5.8. to A5.14
- Appendices 6 to 7
Appendix 5: Modelling results for environmental properties of industry-restricted HFOs
Table A5.1. Results of the Level III fugacity modelling (EQC 2003)
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C9 | Air | Water | Soil | Sediment |
Air | 99.5 | 0.03 | 0.5 | 0.02 |
Water | 1.5 | 48 | 0 | 50.5 |
Soil | 0.1 | 0 | 99.9 | 0 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C15 | Air | Water | Soil | Sediment |
Air | 98.4 | 0.01 | 1.5 | 0.1 |
Water | 0.01 | 8.7 | 0 | 91.3 |
Soil | 0.1 | 0.002 | 99.9 | 0.02 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 13.7 | 0.9 | 66.5 | 18.8 |
Water | 0 | 4.6 | 0 | 95.4 |
Soil | 0 | 0.002 | 99.9 | 0.04 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C30 | Air | Water | Soil | Sediment |
Air | 0.6 | 0.4 | 79.9 | 19.2 |
Water | 0 | 1.9 | 0 | 98.1 |
Soil | 0 | 0.002 | 99.9 | 0.1 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C50 | Air | Water | Soil | Sediment |
Air | 0.03 | 0.02 | 97.3 | 2.7 |
Water | 0 | 0.9 | 0 | 99.1 |
Soil | 0 | 0.003 | 99.7 | 0.3 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C9 | Air | Water | Soil | Sediment |
Air | 99.8 | 0 | 0.2 | 0 |
Water | 3.3 | 85.7 | 7.0E-3 | 11 |
Soil | 6.2 | 9.0E-3 | 93.7 | 1.0E-3 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C15 | Air | Water | Soil | Sediment |
Air | 99 | 0.001 | 1.0 | 0.01 |
Water | 0.01 | 9.6 | 0.0 | 90.4 |
Soil | 0.04 | 0.001 | 99.9 | 0.01 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 94 | 0.05 | 5.1 | 0.9 |
Water | 0 | 5 | 0 | 95 |
Soil | 0 | 0.002 | 99.9 | 0.03 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C30 | Air | Water | Soil | Sediment |
Air | 69.7 | 0.2 | 18.1 | 12.1 |
Water | 0 | 1.3 | 0 | 98.7 |
Soil | 0.1 | 0.003 | 99.7 | 0.2 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C50 | Air | Water | Soil | Sediment |
Air | 0.03 | 0.03 | 96.7 | 3.3 |
Water | 0 | 0.9 | 0 | 99.1 |
Soil | 0 | 0.003 | 99.7 | 0.3 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C9 | Air | Water | Soil | Sediment |
Air | 99.8 | 0 | 0.2 | 0 |
Water | 2.8 | 93.4 | 3.8 | 0 |
Soil | 3.2 | 9.0E-3 | 96.8 | 0 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C15 | Air | Water | Soil | Sediment |
Air | 97.3 | 0.03 | 2.3 | 0.4 |
Water | 0.006 | 7 | 0 | 93 |
Soil | 0.002 | 0.002 | 99.9 | 0.02 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 46.5 | 1.4 | 15.7 | 36.4 |
Water | 0 | 3.7 | 0 | 96.3 |
Soil | 0 | 0.002 | 99.9 | 0.05 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C30 | Air | Water | Soil | Sediment |
Air | 4.5 | 0.3 | 77.1 | 18.1 |
Water | 0 | 1.9 | 0 | 98.2 |
Soil | 0 | 0.002 | 99.9 | 0.1 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C50 | Air | Water | Soil | Sediment |
Air | 0.03 | 0.03 | 96.7 | 3.3 |
Water | 0 | 0.9 | 0 | 99.1 |
Soil | 0 | 0.003 | 99.7 | 0.3 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C9 | Air | Water | Soil | Sediment |
Air | 99.0 | 0.2 | 0.8 | 0.01 |
Water | 2.7 | 88.8 | 0.02 | 8.5 |
Soil | 2 | 0.1 | 97.9 | 0.01 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C15 | Air | Water | Soil | Sediment |
Air | 96.8 | 0.008 | 3 | 0.1 |
Water | 0.05 | 6 | 0 | 94 |
Soil | 0.06 | 0.002 | 99.9 | 0.04 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 70.5 | 0.1 | 20.7 | 8.7 |
Water | 0 | 1.3 | 0 | 98.7 |
Soil | 0 | 0.002 | 99.8 | 0.2 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C30 | Air | Water | Soil | Sediment |
Air | 2.7 | 0.05 | 92.1 | 5.2 |
Water | 0 | 0.9 | 0 | 99.1 |
Soil | 0 | 0.003 | 99.7 | 0.3 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C50 | Air | Water | Soil | Sediment |
Air | 0.2 | 0.15 | 87.4 | 12.3 |
Water | 0 | 1.2 | 0 | 98.8 |
Soil | 0 | 0.003 | 99.8 | 0.2 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C14 | Air | Water | Soil | Sediment |
Air | 93.1 | 0.2 | 6.0 | 0.8 |
Water | 0.2 | 18.1 | 0.02 | 81.6 |
Soil | 0.03 | 0 | 99.9 | 0.03 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C18 | Air | Water | Soil | Sediment |
Air | 7.7 | 0.6 | 60.4 | 31.2 |
Water | 0 | 2.0 | 0.05 | 97.9 |
Soil | 0 | 0.004 | 99.8 | 0.2 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C22 | Air | Water | Soil | Sediment |
Air | 3.0 | 0.05 | 91.8 | 5.2 |
Water | 0 | 1.0 | 0.02 | 99.0 |
Soil | 0 | 0 | 99.7 | 0.3 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C9 | Air | Water | Soil | Sediment |
Air | 99.4 | 0.3 | 0.3 | 0 |
Water | 4.4 | 94.6 | 0.01 | 0.9 |
Soil | 1.0 | 0.1 | 98.9 | 0 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C15 | Air | Water | Soil | Sediment |
Air | 98.4 | 0.05 | 1.1 | 0.4 |
Water | 0.03 | 11.5 | 0 | 88.5 |
Soil | 0.001 | 0.001 | 99.9 | 0.01 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 63.2 | 0.5 | 28.3 | 8 |
Water | 0 | 5.6 | 0 | 94.4 |
Soil | 0 | 0.002 | 99.9 | 0.03 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C30 | Air | Water | Soil | Sediment |
Air | 4.7 | 0.2 | 79.5 | 15.5 |
Water | 0 | 1.5 | 0 | 98.5 |
Soil | 0 | 0.002 | 99.8 | 0.2 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C50 | Air | Water | Soil | Sediment |
Air | 0.1 | 0.08 | 91.9 | 7.9 |
Water | 0 | 1 | 0 | 99 |
Soil | 0 | 0.003 | 99.7 | 0.27 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C10 | Air | Water | Soil | Sediment |
Air | 99.8 | 0.2 | 0.05 | 0.0002 |
Water | 2.0 | 97.8 | 0.001 | 0.1 |
Soil | 0.2 | 0.02 | 99.8 | 0.00002 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C15 | Air | Water | Soil | Sediment |
Air | 81.4 | 1.7 | 1.5 | 15.4 |
Water | 0.2 | 9.7 | 0.004 | 90.0 |
Soil | 0.002 | 0.004 | 100 | 0.04 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 24.7 | 0.9 | 24.3 | 50 |
Water | 0.005 | 1.78 | 0.005 | 98.2 |
Soil | 0.0 | 0.002 | 99.9 | 0.1 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C15 | Air | Water | Soil | Sediment |
Air | 65.3 | 6 | 9.6 | 19 |
Water | 0.4 | 23.9 | 0.06 | 75.6 |
Soil | 0.001 | 0.009 | 99.9 | 0.03 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 47 | 1.4 | 33 | 18.6 |
Water | 0 | 7 | 0 | 93 |
Soil | 0 | 0.002 | 99.9 | 0.02 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C30 | Air | Water | Soil | Sediment |
Air | 3.6 | 0.4 | 77.6 | 18.5 |
Water | 0 | 1.9 | 0 | 98.1 |
Soil | 0 | 0.002 | 99.9 | 0.1 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C50 | Air | Water | Soil | Sediment |
Air | 0.2 | 0.2 | 86.7 | 12.9 |
Water | 0 | 1.2 | 0 | 98.8 |
Soil | 0 | 0.003 | 99.8 | 0.2 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C12 | Air | Water | Soil | Sediment |
Air | 91.6 | 6.7 | 1.4 | 0.4 |
Water | 0.4 | 94.1 | 0.006 | 5.5 |
Soil | 0.002 | 0.04 | 100 | 0.002 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C15 | Air | Water | Soil | Sediment |
Air | 92.6 | 4.2 | 1.7 | 1.5 |
Water | 1.5 | 72.6 | 0.028 | 25.9 |
Soil | 0.001 | 0.005 | 100 | 0.002 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 94.1 | 0.6 | 4.6 | 0.7 |
Water | 0.07 | 44.8 | 0.003 | 55.1 |
Soil | less than 0.001 | less than 0.001 | 100 | less than 0.001 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C15 | Air | Water | Soil | Sediment |
Air | 68.5 | 9.73 | 11.6 | 10.2 |
Water | 0.1 | 48.7 | 0.02 | 51.2 |
Soil | 0 | 0.01 | 99.98 | 0.01 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 41.7 | 2.6 | 9.6 | 46.0 |
Water | 0.001 | 5.4 | 0 | 94.6 |
Soil | 0 | 0.002 | 99.99 | 0.03 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C30 | Air | Water | Soil | Sediment |
Air | 1.2 | 0.3 | 81.3 | 17.2 |
Water | 0 | 1.6 | 0 | 98.4 |
Soil | 0 | 0.002 | 99.9 | 0.1 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C50 | Air | Water | Soil | Sediment |
Air | 0.009 | 0.01 | 98.8 | 1.2 |
Water | 0 | 0.9 | 0 | 99.1 |
Soil | 0 | 0.003 | 99.7 | 0.3 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C16 | Air | Water | Soil | Sediment |
Air | 13.1 | 4.7 | 58.1 | 24.1 |
Water | 0 | 16.2 | 0.04 | 83.7 |
Soil | 0 | 0 | 99.9 | 0.1 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 0.3 | 0.4 | 86.6 | 12.6 |
Water | 0.0 | 3.0 | 0.0 | 97.0 |
Soil | 0 | 0 | 99.8 | 0.2 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C20 | Air | Water | Soil | Sediment |
Air | 0.65 | 0.36 | 85.1 | 13.9 |
Water | 0 | 2.6 | 0.002 | 97.4 |
Soil | 0 | 0.005 | 99.8 | 0.2 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C30 | Air | Water | Soil | Sediment |
Air | 0.06 | 0.05 | 95 | 4.9 |
Water | 0 | 0.9 | 0 | 99.1 |
Soil | 0 | 0.003 | 99.7 | 0.3 |
Compartment of release (100%) | Percentage of substance partitioning into each compartment | |||
---|---|---|---|---|
C22 | Air | Water | Soil | Sediment |
Air | 0.3 | 0.3 | 83.7 | 15.6 |
Water | 0 | 2.1 | 0 | 97.9 |
Soil | 0 | 0 | 99.9 | 0.1 |
Table A5.2. Modelled data for primary (BioHCWin 2008; BIOWIN4 2009) and ultimate (BIOWIN3, 5 and 6 2009; CATABOL; TOPKAT) degradation of HFO components
Alkanes | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C9 n-nonane | 7 | 4.20 |
C15 pentadecane | 19 | 4.08 |
C20 eicosane | 40 | 3.98 |
C30 triacontane | 143 | 3.78 |
C50 | 4581 | 3.37 |
Isoalkanes | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C9 2,3-dimethylheptane | 8 | 3.93 |
C15 2-methyltetradecane | 17 | 3.81 |
C20 3-methylnonadecane | 36 | 3.71 |
C30 hexamethyltetracosane | 333 | 3.24 |
C50 | 3504 | 3.37 |
One-ring cycloalkanes | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C9 1,2,3-trimethylcyclohexane | 4 | 3.67 |
C15 nonylcyclohexane | 25 | 3.81 |
C20 tetradecylcyclohexane | 53 | 3.71 |
C30 1,5-dimethyl-1-(3,7,11,15-tetramethyl-octadecyl)cyclohexane | 154 | 3.24 |
C50 | 660 | 4.18 |
Two-ring cycloalkanes | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C9 cis-bicyclononane | 56 | 3.67 |
C15 2-isopentadecylin | 88 | 3.55 |
C20 2,4-dimethyloctyl-2-decalin | 250 | 3.56 |
C30 2,4,6,10,14-pentamethyldodecyl-2-decalin | 1761 | 3.51 |
C50 | 494 | 4.99 |
Polycycloalkanes | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C14 hydrophenanthrene | 117 | 3.57 |
C18 hydrochrysene | 678 | 3.49 |
C22 hydropicene | 4416 | 3.41 |
One-ring aromatics | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C9 ethylmethylbenzene | 5 | 3.54 |
C15 2-nonylbenzene | 14 | 3.76 |
C20 tetradecylbenzene | 31 | 3.66 |
C30 1-benzyl-4,8,12,16-tetramethyleicosane | 252 | 3.45 |
C50 | 1594 | 3.65 |
Cycloalkane monoaromatics | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C10 tetralin | 1.46 | 3.52 |
C15 methyloctahydro-phenanthrene | 466 | 3.42 |
C20 ethyldodecahydro-chyrsene | 469 | 3.32 |
Two-ring aromatics | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C15 4-isopropylbiphenyl | 8 | 3.50 |
C20 2-isodecylnaphthalene | 24 | 3.66 |
C30 2-(4,8,14,18-tetramethyl-hexadecyl)naphthalene | 145 | 3.46 |
C50 | 444 | 4.46 |
Cycloalkane diaromatics | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C12 acenaphthene | 18.8 | 3.49 |
C15 ethylfluorene | 16.5 | 3.50 |
C20 isoheptylfluorene | 40.9 | 3.33 |
Three-ring PAHs | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C15 2-methylphenanthrene | 24 | 3.50 |
C20 2-isohexylphenanthrene | 35 | 3.40 |
C30 2-(2,4,10-trimethyl-tridecyl)phenanthrene | 212 | 3.20 |
C50 alkylated anthracene | 12 690 | 3.66 |
Four-ring PAHs | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C16 fluoranthene | 191 | 2.85 |
C20 benzo[k]fluoranthene | 285 | 2.78 |
Five-ring PAHs | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C20 benzo[a]pyrene | 422 | 2.78 |
C30 dimethyloctyl- benzo[a]pyrene | 2076 | 2.51 |
Six-ring PAHs | Primary Degradation BioHCWin (2008) [a] (days) | Primary Degradation BIOWIN 4 (2009) Expert Survey[b] |
---|---|---|
C22 benzo[ghi]perylene | 517 | 2.75 |
Table A5.2 cont. Modelled data for primary (BioHCWin 2008; BIOWIN4 2009) and ultimate (BIOWIN3, 5 and 6 2009; CATABOL; TOPKAT) degradation of HFO components[a]
Alkanes | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C9 n-nonane | 3.51 | 0.68 | 0.87 | 99.95 | 1 | less than 182 |
C15 pentadecane | 3.33 | 0.72 | 0.88 | 99.94 | 1 | less than 182 |
C20 eicosane | 3.17 | 0.76 | 0.89 | 89 | 1 | less than 182 |
C30 triacontane | 2.86 | 0.84 | 0.92 | 100 | 1 | less than 182 |
C50 | 2.24 | 0.99 | 0.95 | 100 | 1 | less than 182 |
Isoalkanes | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C9 2,3-dimethylheptane | 3.21 | 0.38 | 0.50 | 9.45 | 1 | less than 182 |
C15 2-methyltetra-decane | 3.03 | 0.57 | 0.75 | 91.11 | 1 | less than 182 |
C20 3-methyl-nonadecane | 2.87 | 0.61 | 0.77 | 91 | 1 | less than 182 |
C30 hexamethyl-tetracosane | 2.26 | -0.06 | 0.04 | 5.1 | 0[*] | greater than or equal to 182 |
C50 | 2.24 | 0.84 | 0.87 | 89.9 | 1 | greater than or equal to 182d |
One-ring cycloalkanes | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C9 1,2,3-trimethyl-cyclohexane | 2.92 | 0.43 | 0.32 | 2.64 | 0.011[*] | less than 182 |
C15 nonyl-cyclohexane | 3.04 | 0.57 | 0.65 | 57.9 | 1 | less than 182 |
C20 tetradecyl-cyclohexane | 2.88 | 0.63 | 0.75 | 64.1 | 1 | less than 182 |
C30 1,5-dimethyl-1-(3,7,11,15-tetramethyl-octadecyl)-cyclohexane | 2.27 | -0.0007 | 0.02 | 3.5 | 0[*] | greater than or equal to 182 |
C50 | 3.14 | 0.64 | 0.22 | 69.2 | 0[*] | greater than or equal to 182 d |
Two-ring cycloalkanes | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C9 cis-bicyclononane | 2.92 | 0.51 | 0.58 | 0 | 0.001 | less than 182 |
C15 2-isopentadecylin | 2.74 | 0.32 | 0.19 | 1.8 | 0 | greater than or equal to 182 |
C20 2,4-dimethyl-octyl-2-decalin | 2.67 | 0.45 | 0.26 | 4.5 | 0 | greater than or equal to 182 |
C30 2,4,6,10,14- pentamethyl-dodecyl- 2-decalin | 2.57 | -0.16 | 0.01 | 4.6 | 0[*] | greater than or equal to 182 |
C50 | 4.04 | 0.34 | 0.01 | 6.4 | 0[*] | greater than or equal to 182 |
Polycycloalkanes | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C14 hydro-phenanthrene | 2.77 | 0.39 | 0.24 | 0 | 0[*] | greater than or equal to 182 |
C18 hydrochrysene | 2.65 | 0.29 | 0.07 | 0 | 0[*] | greater than or equal to 182 |
C22 hydropicene | 2.54 | 0.19 | 0.02 | 0 | 0[*] | greater than or equal to 182 |
One-ring aromatics | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C9 ethylmethyl-benzene | 2.78 | 0.37 | 0.44 | 10.67[*] | 0.086 | less than 182 |
C15 2-nonylbenzene | 2.99 | 0.44 | 0.53 | 50.9 | 0.11 | less than 182 |
C20 tetradecyl-benzene | 2.84 | 0.47 | 0.56 | 90.6 | 0.001[*] | less than 182 |
C30 1-benzyl-4,8,12,16-tetramethyl-eicosane | 2.53 | -0.05 | 0.04 | 5.1 | 0[*] | greater than or equal to 182 |
C50 | 2.56 | 0.22 | 0.09 | 70 | 0.2[*] | greater than or equal to 182 d |
Cycloalkane monoaromatics | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C10 tetralin | 2.76 | 0.28 | 0.36 | 0.71 | 0.003 | less than 182 |
C15 methyl-octahydro-phenanthrene | 2.61 | 0.19 | 0.13 | 0.91[*] | 0 | greater than or equal to 182 |
C20 ethyl-dodecahydro-chyrsene | 2.46 | 0.10 | 0.04 | 2.91 | 0[*] | greater than or equal to 182 |
Two-ring aromatics | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C15 4-isopropyl-biphenyl | 2.71 | 0.19 | 0.15 | 12.16 | 0[*] | greater than or equal to 182 |
C20 2-isodecyl-naphthalene | 2.83 | 0.16 | 0.12 | 3.8 | 0[*] | greater than or equal to 182 |
C30 2-(4,8,14,18-tetramethyl- hexadecyl)-naphthalene | 2.52 | -0.06 | 0.03 | 4.6 | 0[*] | greater than or equal to 182 |
C50 | 3.46 | -0.59 | 0.0004 | 3.4 | 0[*] | greater than or equal to 182 |
Cycloalkane diaromatics | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C12 acenaphthene | 2.71 | 0.19 | 0.19 | 3.82 | 0 | greater than or equal to 182 |
C15 ethylfluorene | 2.70 | 0.15 | 0.10 | 1.03[*] | 0 | less than 182 |
C20 isoheptyl-fluorene | 2.47 | -0.03 | 0.036 | 2.36[*] | 0.916 | less than 182 |
Three-ring PAHs | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C15 2-methyl- phenanthrene | 2.70 | 0.26 | 0.16 | 21.2[*] | 0.004 | less than 182 |
C20 2-isohexyl-phenanthrene | 2.54 | -0.0012 | 0.036 | 3.99[*] | 0.302 | greater than or equal to 182 |
C30 2-(2,4,10-trimethyl-tridecyl)-phenanthrene | 2.23 | -0.22 | 0.01 | 5.6 | 0[*] | greater than or equal to 182 |
C50 alkylated anthracene | 2.58 | -0.11 | 0.01 | 56.6 | 0[*] | greater than or equal to 182 d |
Four-ring PAHs | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C16 fluoranthene | 1.95 | 0.19 | 0.11 | 19.67[*] | 0 | greater than or equal to 182 |
C20 benzo[k]-fluoranthene | 1.84 | 0.06 | 0.035 | 9.3 | 0 | greater than or equal to 182 |
Five-ring PAHs | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C20 benzo[a]pyrene | 1.84 | 0.06 | 0.035 | 9.29[*] | 0[*] | greater than or equal to 182 |
C30 dimethyloctyl- benzo[a]pyrene | 1.46 | -0.32 | 0.002 | 6.6 | 0[*] | greater than or equal to 182 |
Six-ring PAHs | BIOWIN 3 (2009) Expert Survey[b] | BIOWIN 5 (2009) MITI linear probability[c] | BIOWIN 6 (2009) MITI non-linear probability[c] | CATABOL (2008) % BOD | TOPKAT (2004) Probability of biodegrad-ability | Extrapolated half-life compared with criteria (days) |
---|---|---|---|---|---|---|
C22 benzo[ghi]-perylene | 1.79 | -0.011 | 0.018 | 2.9 | 0[*] | greater than or equal to 182 |
Abbreviations: BOD, biological oxygen demand; MITI, Ministry of International Trade & Industry, Japan
[a] Half-life estimations are for non-specific media (i.e., water, soil and sediment).
[b] Output is a numerical score from 0–5.
[c] Output is a probability score.
[d] Extrapolated half-life compared with criteria (days) based on BioHCWin results (2008).
[*] Modelled results were found to be out of domain and therefore not considered for persistence. For modelled results of CATABOL that were found to be out of domain, it was assumed that results for TOPKAT, BIOWIN 5, 6 were also out of domain because these models use the same dataset. In these cases, only BIOWIN 3, 4 and BioHCWin were considered when determining the persistence of the component.
Table A5.3. Potential presence of persistent representative structures
Isoalkanes | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C30 | Yes | Yes | Yes | Yes | Yes |
C50 | Yes | Yes |
One-ring cycloalkanes | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C30 | Yes | Yes | Yes | Yes | Yes |
C50 | Yes |
Two-ring cycloalkanes | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C15 | Yes | ||||
C20 | Yes | Yes | Yes | Yes | |
C30 | Yes | Yes | Yes | Yes | Yes |
C50 | Yes |
Polycycloalkanes | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C14 | Yes | Yes | Yes | ||
C18 | Yes | Yes | Yes | Yes | |
C22 | Yes | Yes | Yes | Yes | Yes |
One-ring aromatics | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C30 | Yes | Yes | Yes | Yes | Yes |
C50 | Yes |
Cycloalkane monoaromatics | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C15 | Yes | Yes | Yes | Yes | |
C20 | Yes | Yes | Yes | Yes | Yes |
Two-ring aromatics | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C15 | Yes | Yes | Yes | Yes | |
C20 | Yes | Yes | Yes | Yes | Yes |
C30 | Yes | Yes | Yes | Yes | Yes |
C50 | Yes |
Cycloalkane diaromatics | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C12 | Yes | Yes | Yes | Yes |
Three-ring aromatics | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C20 | Yes | Yes | Yes | Yes | Yes |
C30 | Yes | Yes | Yes | Yes | Yes |
C50 | Yes |
Four-ring aromatics | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C16 | Yes | Yes | Yes | Yes | Yes |
C20 | Yes | Yes | Yes | Yes | Yes |
Five-ring aromatics | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C20 | Yes | Yes | Yes | Yes | Yes |
C30 | Yes | Yes | Yes | Yes |
Six-ring aromatics | CAS RN 64741-75-9 | CAS RN 68789-08-4 | CAS RN 70592-76-6 | CAS RN 70592-77-7 | CAS RN 70592-78-8 |
---|---|---|---|---|---|
C22 | Yes | Yes | Yes | Yes | Yes |
Table A5.4. Proportion (weight %) of persistent representative structures in three samples of Fuel Oil No. 6 (Fuhr 2008)
Boiling point (°C) | Weight % Sample A | Weight % Sample B | Weight % Sample C | Weight % Average | |
---|---|---|---|---|---|
Isoalkane C50 | 548 | 6.8 | 4 | 10.1 | 7.0 |
One-ring cycloalkane C50 | 699 | 6.8 | 4 | 10.1 | 7.0 |
Two-ring cycloalkane C50 | 687 | 6.8 | 4 | 10.1 | 7.0 |
One-ring aromatic C50 | 697 | 22.1 | 21.3 | 24.3 | 22.6 |
Two-ring aromatic C50 | 722 | 22.1 | 21.3 | 24.3 | 22.6 |
Three-ring aromatic C50 | 746 | 22.1 | 21.3 | 24.3 | 22.6 |
Five-ring aromatic C30 | 545 | 22.1 | 21.3 | 24.3 | 22.6 |
Six-ring aromatic C22 | greater than 500 | 22.1 | 21.3 | 24.3 | 22.6 |
Boiling point (°C) | Weight % Sample A | Weight % Sample B | Weight % Sample C | Weight % Average | |
---|---|---|---|---|---|
Isoalkanes C30 | 350 | 8.3 | 2.8 | 3.5 | 4.9 |
One-ring cycloalkanes C30 | 421 | 3.4 | 2.0 | 1.9 | 2.4 |
Two-ring cycloalkanes C15 | 244 | 2.9 | 1.8 | 1.8 | 2.2 |
Two-ring cycloalkanes C20 | 339 | 2.9 | 1.8 | 1.8 | 2.2 |
Two-ring cycloalkanes C30 | 420 | 2.9 | 1.8 | 1.8 | 2.2 |
Polycycloalkanes C14 | 225 | 2.8 | 2.2 | 3.2 | 2.7 |
Polycycloalkanes C18 | 316 | 2.8 | 2.2 | 3.2 | 2.7 |
Polycycloalkanes C22 | 365 | 2.8 | 2.2 | 3.2 | 2.7 |
One-ring aromatics C30 | 437 | 1.7 | 4.2 | 2.2 | 2.7 |
Cycloalkane monoaromatics C15 | 285 | 2.2 | 4.3 | 2.6 | 3.0 |
Cycloalkane monoaromatics C20 | 351 | 2.2 | 4.3 | 2.6 | 3.0 |
Two-ring aromatics C15 | 308 | 1.1 | 6.0 | 4.5 | 3.9 |
Two-ring aromatics C20 | 373 | 1.1 | 6.0 | 4.5 | 3.9 |
Two-ring aromatics C30 | 469 | 1.1 | 6.0 | 4.5 | 3.9 |
Cycloalkane diaromatics C12 | 279 | 0.8 | 1.7 | 2.4 | 1.6 |
Three-ring aromatics C20 | 398 | 0.9 | 2.3 | 3.9 | 2.4 |
Three-ring aromatics C30 | 493 | 0.9 | 2.3 | 3.9 | 2.4 |
Four-ring aromatics C16 | 384 | 1.2 | 1.4 | 2.7 | 1.8 |
Four-ring aromatics C20 | 480 | 0.6 | 0.5 | 0.6 | 0.6 |
Five-ring aromatics C20 | 495 | 0.4 | 0.4 | 0.2 | 0.3 |
Totals | 55.2 | 54.9 | 63.9 | 58.1 |
Table A5.5. Modelled atmospheric degradation of representative structures for HFOs via reaction with hydroxyl radicals (AOPWIN 2008)
Alkanes | Half-life (days) [a] OH• |
---|---|
C9 | 1.1 |
C15 | 1 |
C20 | 0.4 |
C30 | 0.3 |
C50 | 0.2 |
Isoalkanes | Half-life (days) [a] OH• |
---|---|
C9 | 1.1 |
C15 | 0.6 |
C20 | 0.4 |
C30 | 0.3 |
C50 | 0.2 |
One-ring cycloalkanes | Half-life (days) [a] OH• |
---|---|
C9 | 0.8 |
C15 | 0.5 |
C20 | 0.4 |
C30 | 0.2 |
C50 | 0.2 |
Two-ring cycloalkanes | Half-life (days) [a] OH• |
---|---|
C9 | 0.8 |
C15 | 0.4 |
C20 | 0.3 |
C30 | 0.2 |
C50 | 0.1 |
Polycycloalkanes | Half-life (days) [a] OH• |
---|---|
C14 | 0.4 |
C18 | 0.3 |
C22 | 0.2 |
One-ring aromatics | Half-life (days) [a] OH• |
---|---|
C9 | 1.4 |
C15 | 0.7 |
C20 | 0.5 |
C30 | 0.3 |
C50 | 0.2 |
Cycloalkane monoaromatics | Half-life (days) [a] OH• |
---|---|
C10 | 0.3 |
C15 | 0.5 |
C20 | 0.3 |
Two-ring aromatics | Half-life (days) [a] OH• |
---|---|
C15 | 0.2 |
C20 | 0.2 |
C30 | 0.1 |
C50 | 0.1 |
Cycloalkane diaromatics | Half-life (days) [a] OH• |
---|---|
C12 | 0.2 |
C15 | 0.6 |
C20 | 0.5 |
Three-ring PAHs | Half-life (days) [a] OH• |
---|---|
C15 | 0.3 |
C20 | 0.3 |
C30 | 0.2 |
C50 | 0.1 |
Four-ring PAHs | Half-life (days) [a] OH• |
---|---|
C16 | 0.4 |
C20 | 0.2 |
Five-ring PAHs | Half-life (days) [a] OH• |
---|---|
C20 | 0.2 |
C30 | 0.1 |
Six-ring PAHs | Half-life (days) [a] OH• |
---|---|
C22 | 0.1 |
Table A5.6. Experimental BAFs for aromatic hydrocarbons
One-ring aromatics | Reference; Study | Log Kow | BAF experimental (L/kg ww) |
---|---|---|---|
C6 benzene | Zhou et al. 1997 Atlantic salmon (white muscle); 96-hour (WSF of crude oil) | 2.13 (expt.) | 4 |
C7 toluene | Zhou et al. 1997 Atlantic salmon (white muscle); 96-hour (WSF of crude oil) | 2.73 (expt.) | 11 |
C8 ethylbenzene | Zhou et al. 1997 Atlantic salmon (white muscle); 96-hour (WSF of crude oil) | 3.15 (expt.) | 26 |
C8 xylenes | Zhou et al. 1997 Atlantic salmon (white muscle); 96-hour (WSF of crude oil) | 3.12 (expt.) | 47 |
C9 isopropylbenzene | Zhou et al. 1997 Atlantic salmon (white muscle); 96-hour (WSF of crude oil) | 3.66 (expt.) | 20 |
C9 propylbenzene | Zhou et al. 1997 Atlantic salmon (white muscle); 96-hour (WSF of crude oil) | 3.69 (expt.) | 36 |
C9 ethylmethylbenzene | Zhou et al. 1997 Atlantic salmon (white muscle); 96-hour (WSF of crude oil) | 3.98 (expt.) | 51 |
C9 trimethylbenzene | Zhou et al. 1997 Atlantic salmon (white muscle); 96-hour (WSF of crude oil) | 3.66 (expt.) | 74 |
One-ring aromatics | Reference; Study | Log Kow | BAF experimental (L/kg ww) |
---|---|---|---|
C10 naphthalene | Neff et al. 1976 Clam; 24-hour (oil-in-water dispersion of No. 2 fuel oil) lab study | 3.30 (expt.) | 2.3 |
C11 methyl naphthalenes | Zhou et al. 1997 Atlantic salmon (white muscle); 96-hour (WSF of crude oil) lab study | 3.87 (expt.) | 230 |
C11 1-methylnaphthalene | Neff et al. 1976 Clam; 24-hour (oil-in-water dispersion of No. 2 fuel oil) lab study | 3.87 (expt.) | 8.5 |
C11 2-methylnaphthalene | Neff et al. 1976 Clam; 24-hour (oil-in-water dispersion of No. 2 fuel oil) lab study | 3.86 (expt.) | 8.1 |
C12 dimethylnaphthalene | Neff et al. 1976 Clam; 24-hour (oil-in-water dispersion of No. 2 fuel oil) lab study | 4.31 (expt.) | 17.1 |
C13 trimethylnaphthalene | Neff et al. 1976 Clam; 24-hour (oil-in-water dispersion of No. 2 fuel oil) lab study | 4.81 | 26.7 |
One-ring aromatics | Reference; Study | Log Kow | BAF experimental (L/kg ww) |
---|---|---|---|
C14 phenanthrene | Burkhard and Lukasewycz 2000 Lake trout; field study | 4.57 | 87 |
C16 fluoranthene | Burkhard and Lukasewycz 2000 Lake trout; field study | 5.23 | 1550 |
C18 chrysene | Burkhard and Lukasewycz 2000 Lake trout; field study | 5.81 | 3990 |
Abbreviation: (expt.), experimental log Kow data
Table A5.7. Summary of empirical aquatic bioconcentration factors (BCFs) for various PAHs (adapted from European Commission 2008b)
Substance | Species | Exposure time | BCF (L/kg ww) | Reference |
---|---|---|---|---|
fluoranthene | Pimephales promelas (fathead minnow) | 24 hours | 9054 | Weinstein and Oris 1999 |
pyrene | Poecilia reticulate (guppy) | 48 hours | 11 300 | De Voogt et al. 1991 |
pyrene | Cyprinodon variegatus (sheepshead minnow) | 36 days | 145[a], 97[b] | Jonsson et al. 2004 |
benzo[a]pyrene | Lepomis macrochirus (bluegill sunfish) | 48 hours | 608 | Jimenez et al. 1987 |
Substance | Species | Exposure time | BCF (L/kg ww) | Reference |
---|---|---|---|---|
fluoranthene | Mytilus edulis (blue mussel) | 96 hours | 5920 | McLeese and Burridge 1987 |
fluoranthene | Mya arenaria (clam) | 96 hours | 4120 | McLeese and Burridge 1987 |
pyrene | M. edulis | 96 hours | 4430 | McLeese and Burridge 1987 |
pyrene | M. arenaria | 96 hours | 6430 |
Substance | Species | Exposure time | BCF (L/kg ww) | Reference |
---|---|---|---|---|
fluoranthene | Daphnia magna (water flea) | 24 hours | 1742 | Newsted and Giesy 1987 |
fluoranthene | Cragon septemspinosa (sand shrimp) | 96 hours | 180 | McLeese and Burridge 1987 |
pyrene | D. magna | 24 hours | 2702 | Newsted and Giesy 1987 |
pyrene | C. septemspinosa | 96 hours | 225 | McLeese and Burridge 1987 |
chrysene | D. magna | 24 hours | 6088 | Newsted and Giesy 1987 |
benzo[a]anthracene | D. magna | 24 hours | 2920 | McCarthy et al. 1985 |
benzo[a]anthracene | D. magna | 24 hours | 10 226 | Newsted and Giesy 1987 |
benzo[k]fluoranthene | D. magna | 24 hours | 13 225 | Newsted and Giesy 1987 |
benzo[a]pyrene | D. magna | 24 hours | 12 761 | Newsted and Giesy 1987 |
benzo[e]pyrene | D. magna | 24 hours | 25 200 | Newsted and Giesy 1987 |
benzo[ghi]perylene | D. magna | 24 hours | 28 288 | Newsted and Giesy 1987 |
Substance | Species | Exposure time | BCF (L/kg ww) | Reference |
---|---|---|---|---|
fluoranthene | Nereis virens (sandworm) | 96 hours | 720 | McLeese and Burridge 1987 |
pyrene | N. virens | 96 hours | 700 | McLeese and Burridge 1987 |
[b] High exposure level (72.31 µg/L).
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