Appendices of the Final Screening Assessment Petroleum Sector Stream Approach
Fuel Oil, No. 4
Fuel Oil, No. 6
Fuel Oil, Residual
[Fuels]
Chemical Abstracts Service Registry Numbers
68476-31-3
68553-00-4
68476-33-5
Environment Canada
Health Canada
April 2014
Table of Content
- Appendix A: Petroleum Substance Grouping
- Appendix B: Physical-chemical Data Tables for Fuel Oil No. 4, Fuel Oil No. 6 and Residual Fuel Oil
- Appendix C: Production and Transportation of Fuel Oil No. 6, Fuel Oil No. 4 and Residual Fuel Oil
- Appendix D: Environmental Fate Processes Affecting HFOs
- Appendix E: Persistence and Bioaccumulation
- Appendix F: Ecotoxicological Information
- Appendix G: Summary of Health Effects Information for Fuel Oil No. 4, Fuel Oil No. 6, Residual Fuel Oil and Related HFOs
- Back to the final screening assessment
Appendix A: Petroleum Substance Grouping
| GroupFootnote Appendix A Table A-1[a] | Description | Example |
|---|---|---|
| Crude oils | Complex combinations of aliphatic and aromatic hydrocarbons and small amounts of inorganic compounds, naturally occurring under the Earth’s surface or under the sea floor | Crude oil |
| Petroleum and refinery gases | Complex combinations of light hydrocarbons primarily from C1 to C5 | Propane |
| Low boiling point naphthas | Complex combinations of hydrocarbons primarily from C4 to C12 | Gasoline |
| Gas oils | Complex combinations of hydrocarbons primarily from C9 to C25 | Diesel fuel |
| Heavy fuel oils | Complex combinations of heavy hydrocarbons primarily from C20 to C50 | Fuel Oil No. 6 |
| Base oils | Complex combinations of hydrocarbons primarily from C15 to C50 | Lubricating oils |
| Aromatic extracts | Complex combinations of primarily aromatic hydrocarbons from C15 to C50 | Feedstock for benzene production |
| Waxes, slack waxes and petrolatum | Complex combinations of primarily aliphatic hydrocarbons from C12 to C85 | Petrolatum |
| Bitumen or vacuum residues | Complex combinations of heavy hydrocarbons having carbon numbers greater than C25 | Asphalt |
Appendix B: Physical-chemical Data Tables for Fuel Oil No. 4, Fuel Oil No. 6 and Residual Fuel Oil
Table B-1. Physical-chemical properties for representative structures of Fuel Oil No. 4, Residual Fuel Oil and Fuel Oil No. 6Footnote Appendix B Table B-1 [a]
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)Footnote Appendix B Table B-1 [b] |
|---|---|---|---|---|
| C12 dodecane (112-40-3) |
68476-31-3 | 216.3 (expt.) |
-9.6 (expt.) |
18.0 (expt.) |
| C15 pentadecane (629-62-9) |
68476-31-3 68553-00-4 68476-33-5 |
271 (expt.) |
9.9 (expt.) |
0.5 (expt.) |
| C20 eicosane (112-95-8) |
68476-31-3 68553-00-4 68476-33-5 |
343 (expt.) |
37 (expt.) |
6.2 × 10−4 (expt.) |
| C30 triacontane |
68476-31-3 68553-00-4 68476-33-5 |
450 (expt.) |
65.8 (expt.) | 3.6 × 10−9 (expt.) |
| C50 | 68476-31-3 68553-00-4 68476-33-5 |
548 (expt.) |
87 (expt.) |
2 × 10−7 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C12 2,3-dimethyl decane (17312-44-6) |
- | 181.4 | -43.0 | 165.0 |
| C15 2-methyl tetradecane (1560-95-8) |
68476-31-3 68553-00-4 68476-33-5 |
250 | 1.5 | 5.8 |
| C20 3-methyl nonadecane (6418-45-7) |
68476-31-3 68553-00-4 68476-33-5 |
326 | 40.0 | 0.1 |
| C30 hexamethyl tetracosane (111-01-3) |
68476-31-3 68553-00-4 68476-33-5 |
408 | 75.0 | 0.04 |
| C50 | - | 675.5 | 294.6 | 5.1 × 10−10 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C12 n-hexylcyclo hexane (4292-75-5) |
- | 224 (expt.) |
-43 (expt.) |
15.2 (expt.) |
| C15 nonylcyclo hexane (2883-02-5) |
68476-31-3 68553-00-4 68476-33-5 |
282 (expt.) |
-10 (expt.) |
0.3 (expt.) |
| C20 tetradecylcyclohexane (1795-18-2) |
68476-31-3 68553-00-4 68476-33-5 |
360 (expt.) |
24 (expt.) |
0.02 |
| C30 1,5-dimethyl-1-(3,7,11,15-tetramethyl octadecyl) cyclohexane |
68476-31-3 68553-00-4 68476-33-5 |
421 | 103 | 1.5 × 10−4 |
| C50 | 68553-00-4 | 674 | 294 | 5.6 × 10−13 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C12 dicyclohexyl (92-51-3) |
68476-31-3 68553-00-4 68476-33-5 |
238 (expt.) |
4 (expt.) |
14.4 (expt.) |
| C15 pentamethyldecalin (91-17-8) | 68476-31-3 68553-00-4 68476-33-5 |
187.3 (expt.) | -30.3 (expt.) | 163 (expt.) |
| C20 2,4-dimethyl octyl-2-decalin |
68476-31-3 68553-00-4 68476-33-5 |
324 | 41 | 0.1 |
| C30 2,4,6,10,14 pentamethyl dodecyl-2-decalin |
68476-31-3 68553-00-4 68476-33-5 |
420 | 106 | 0.0001 |
| C50 | 68553-00-4 | 664 | 289 | 1.2 × 10−18 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C14 hydro-phenanthrene |
68476-31-3 68553-00-4 68476-33-5 |
255 | 21 | 4.5 |
| C18 hydro-chrysene |
68476-31-3 68553-00-4 68476-33-5 |
353 (expt.) |
115 (expt.) |
0.004 |
| C22 hydropicene |
68476-31-3 68553-00-4 68476-33-5 |
365 | 108 | 0.003 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C12 1,2,3-triethyl benzene (42205-08-3) |
68476-31-3 68553-00-4 68476-33-5 |
230 | 11.9 | 10.6 |
| C15 2-nonyl benzene (1081-77-2) |
68476-31-3 68553-00-4 68476-33-5 |
281 (expt.) |
-24 (expt.) |
0.8 (expt.) |
| C20 tetradecyl benzene (1459-10-5) |
68476-31-3 68553-00-4 68476-33-5 |
359 (expt.) |
16 (expt.) |
0.004 (expt.) |
| C20 1-benzyl-4,8-dimethyl-dodecane | 68476-31-3 68553-00-4 68476-33-5 |
334.6 | 49.2 | 0.02 |
| C30 1-benzyl 4,8,12,16 tetramethyl eicosane |
68476-31-3 68553-00-4 68476-33-5 |
437 | 131 | 1.2 × 10−5 |
| C50 | 68553-00-4 | 697 | 305 | 2 × 10−14 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C15 methyl-octahydro-phenanthrene |
68476-31-3 68553-00-4 68476-33-5 |
267 | 28 | 2.3 |
| C20 ethyl-dodecahydro-chyrsene |
68476-31-3 68553-00-4 68476-33-5 |
338 | 82 | 0.02 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C15 4-isopropyl biphenyl (7116-95-2) |
68476-31-3 68553-00-4 68476-33-5 |
309 | 44 | 0.1 |
| C20 2-isodecyl naphthalene |
68476-31-3 68553-00-4 68476-33-5 |
366 | 99 | 0.001 |
| C30 2-(4,8,14,18-tetramethyl hexadecyl) naphthalene |
68476-31-3 68553-00-4 68476-33-5 |
468 | 171 | 7 × 10−7 |
| C50 | 68553-00-4 | 722 | 316 | 3 × 10−15 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C12 acenaphthene (83-32-9) |
68476-31-3 68553-00-4 68476-33-5 |
279 (expt.) |
93.4 (expt.) | 0.3 (expt.) |
| C15 ethylfluorene |
68476-31-3 68553-00-4 68476-33-5 |
338 | 95 | 0.007 |
| C20 isoheptyl fluorene |
68476-31-3 68553-00-4 68476-33-5 |
381 | 126 | 0.0003 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C15 2-methyl phenanthrene (2531-84-2) |
68476-31-3 68553-00-4 68476-33-5 |
155-160 (expt.) |
57-59 (expt.) |
0.009 |
| C20 2-isohexyl phenanthrene |
68476-31-3 68553-00-4 68476-33-5 |
331 | 67 | 0.04 |
| C30 2-(2,4,10-trimethyl tridecyl) phenanthrene |
68476-31-3 68553-00-4 68476-33-5 |
493 | 191.6 | 1 × 10−7 |
| C50 | 68553-00-4 | 746 | 327.5 | 4.87 × 10−16 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C16 fluoranthene |
68476-31-3 68553-00-4 68476-33-5 |
384 (expt.) |
107.8 (expt.) | 1 × 10−3 (expt.) |
| C20 Benzo[k]fluoranthene |
68476-31-3 68553-00-4 68476-33-5 |
480 (expt.) |
217 (expt.) |
1 × 10−7 (expt.) |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C20 benzo[a]pyrene (50-32-8) |
68476-31-3 68553-00-4 68476-33-5 |
495 (expt.) |
177 (expt.) |
7 × 10−7 |
| C30 dimethyloctyl-benzo[a]pyrene |
68476-31-3 68553-00-4 68476-33-5 |
545 | 231 | 2 × 10−9 |
| Chemical class, name (CAS RN) | HFO represented | Boiling point (°C) |
Melting point (°C) |
Vapour pressure (Pa)[b] |
|---|---|---|---|---|
| C22 Benzo[ghi] perylene 191-24-2 |
68476-31-3 68553-00-4 68476-33-5 |
More than 500 (expt.) |
278 (expt.) |
1 × 10−8 (expt.) |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)Footnote Appendix B Table B-1 [c] | Log Kow | Log Koc | Aqueous solubility (mg/L)Footnote Appendix B Table B-1 [d] |
|---|---|---|---|---|
| C12 dodecane (112-40-3) |
8.3 × 105 (expt.) |
6.1 (expt.) |
5.3 | 0.004 (expt.) |
| C15 pentadecane (629-62-9) |
1.3 × 106 (expt.) |
7.7 | 6.7 | 8 × 10−5 (expt.) |
| C20 eicosane (112-95-8) |
2.2 × 107 | 10 | 8.8 | 0.02 (expt.) |
| C30 triacontane |
6.8 × 108 | 15.1 | 13.0 | 8.6 × 10−11 |
| C50 | 3.6 × 1010 | 25 | 21.6 | 2.6 × 10−21 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C12 2,3-dimethyldecane (17312-44-6) |
2 × 106 | 6.1 | 5.3 | 0.1 |
| C15 2-methyl tetradecane (1560-95-8) |
4.6 × 106 | 7.6 | 6.6 | 0.003 |
| C20 3-methyl nonadecane (6418-45-7) |
2.6 × 107 | 10.1 | 8.8 | 1 × 10−5 |
| C30 hexamethyl tetracosane (111-01-3) |
2 × 109 | 14.6 | 12.7 | 2 × 10−10 |
| C50 | 1.5 × 1010 | 25 | 21.5 | 6 × 10−21 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C12 n-heptylcyclo pentane |
1.9 × 105 | 6.1 | 5.3 | 0.1 |
| C15 nonylcyclo hexane (2883-02-5) |
5.3 × 105 | 7.5 | 6.5 | 0.005 |
| C20 tetradecyl cyclohexane (1795-18-2) |
3× 169 | 10.0 | 8.7 | 1.7 × 10−6 |
| C30 1,5-dimethyl-1-(3,7,11,15-tetramethyl octadecyl) cyclohexane |
2.9 × 108 | 14.5 | 12.5 | 4.2 × 10−7 |
| C50 | 2 × 1011 | 24.4 | 21.2 | 1.4 × 10−20 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C12 dicyclohexyl (92-51-3) |
2.6 × 104 | 5.9 | 5.1 | 0.2 |
| C15 pentamethyl decalin (91-17-8) |
4.8 × 104 (expt.) |
4.2 | 3.7 (expt.) |
0.9 (expt.) |
| C20 2,4-dimethyloctyl-2-decalin |
7.2 × 105 | 8.9 | 7.7 | 1.2 × 10−4 |
| C30 2,4,6,10,14 pentamethyl dodecyl-2-decalin |
3.9 × 107 | 13.6 | 11.8 | 1.7 × 10−9 |
| C50 | 5.7 × 1010 | 23.2 | 20.2 | 1.4 × 10−19 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C14 hydrophenanthrene |
8590 | 5.2 | 4.5 | 0.5 |
| C18 hydro-chrysene |
5680 | 6.2 | 5.4 | 0.01 |
| C22 hydro-picene |
3750 | 7.3 | 6.3 | 0.002 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C12 1,2,4-triethylbenzene (877-44-1) |
2480 | 5.1 | 4.4 | 2.9 |
| C15 2-nonylbenzene (1081-77-2) |
1 × 104 | 7.1 (expt.) |
6.1 | 0.03 |
| C20 tetradecylbenzene |
5.7 × 104 | 10 (expt.) | 8.6 | 5 × 10−5 |
| C20 1-benzyl-4,8-dimethyl-dodecane | 8.2 × 104 | 8.8 | 7.6 | 5.5 × 10−4 |
| C30 1-benzyl 4,8,12,16 tetramethyl eicosane |
3.8 × 106 | 13.5 | 12.0 | 7 × 10−9 |
| C50 | 1 × 109 | 23.8 | 21.0 | 2 × 10−19 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C15 methyloctahydro-phenanthrene |
1.5 × 104 | 5.6 | 4.9 | 0.2 |
| C20 ethyldodecahydro-chyrsene |
1.4 × 104 | 7.1 | 6.2 | 0.004 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C15 4-isopropyl biphenyl |
98.7 | 5.5 (expt.) |
4.8 | 0.9 |
| C20 2-isodecyl naphthalene |
1190 | 8.1 | 7.0 | 0.002 |
| C30 2-(4,8,14,18-tetramethyl hexadecyl) naphthalene |
5.4 × 104 | 12.8 | 11.1 | 3 × 10−8 |
| C50 | 8.6 × 106 | 23.2 | 20.2 | 7 × 10−19 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C12 acenaphthene (83-32-9) |
18.6 (expt.) |
3.9 (expt.) | 3.6 (expt.) |
3.9 (expt.) |
| C15 ethylfluorene |
5.6 | 5.1 | 4.4 | 0.2 |
| C20 isoheptylfluorene |
32.7 | 7.5 | 6.5 | 0.0006 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C15 2-methyl phenanthrene (2531-84-2) |
2.8 | 4.9 (expt.) |
4.2 | 0.3 (expt.) |
| C20 2-isohexyl phenanthrene |
9.9 × 104 | 8.0 | 7.0 | 7 × 10−4 |
| C30 2-(2,4,10-trimethyltridecyl) phenanthrene |
942 | 12 | 10 | 1 × 10−8 |
| C50 | 3.1 × 105 | 23.0 | 19.3 | 3.5 × 10−19 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C16 fluoranthene (206-44-0) |
0.9 (expt.) |
5.2 (expt.) |
4.8 (expt.) |
0.26 (expt.) |
| C20 benzo[k]fluoranthene |
0.06 (expt.) |
6.1 (expt.) |
5.6 (expt.) |
0.0008 (expt.) |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C20 benzo[a]pyrene (50-32-8) |
0.05 (expt.) |
6.1 (expt.) |
6.0 (expt.) |
0.002 (expt.) |
| C30 dimethyloctyl-benzo[a]pyrene |
0.8 | 10.9 | 9.5 | 1 × 10−7 |
| Chemical name (CAS RN) |
Henry’s Law constant (Pa*m3/mol)[c] | Log Kow | Log Koc | Aqueous solubility (mg/L)[d] |
|---|---|---|---|---|
| C22 benzo[ghi]perylene (191-24-2) |
0.03 (expt.) |
6.6 (expt.) |
5.8 | 0.0003 (expt.) |
Appendix C: Production and Transportation of Fuel Oil No. 6, Fuel Oil No. 4 and Residual Fuel Oil
| Product | Alberta | Ontario | Quebec | Atlantic | Other provinces and territories |
Canada |
|---|---|---|---|---|---|---|
| Refinery production | 790.0 | 673.7 | 2681.5 | 3788.4 | 324.2 | 8257.6Footnote Appendix C Table C-1a[b] |
| Imports | 0.0 | 60.8 | 316.0 | 869.6 | 521.0 | 1767.4 |
| Exports | 215.2 | 75.3 | 1347.0 | 2784.4 | 128.0 | 4549.8[b] |
| Domestic sales | 47.5 | 699.2 | 2872.2 | 1502.1 | 1275.4 | 6396.4 |
| Regions | 2006 | 2007 | 2008Footnote Appendix C Table C-1b[b] |
|---|---|---|---|
| Atlantic region | 1849 | 2261 | 1663 |
| Quebec | 2491 | 2802 | 2871 |
| Ontario | 1285 | 1228 | 841 |
| West region | 1086 | 1275 | 1257 |
| Canada | 6711 | 7567Footnote Appendix B Table C-1b[c] | 6632 |
| – | Refinery production | Imports | Exports |
|---|---|---|---|
| 2004 | 9154 | 2919 | 3678 |
| 2005 | 8670 | 2740 | 3668 |
| 2006 | 8146 | 1563 | 3714 |
| 2007 | 8617 | 1938 | 4317 |
| 2008 | 8258 | 1767 | 4550 |
| Application | Thousands of cubic metres | Share (%) |
|---|---|---|
| Producer consumption | 503.1 | 7.1 |
| Electricity by utilities | 1115.6 | 15.8 |
| Electricity by industry | 81.2 | 1.2 |
| Steam generation | 49.8 | 0.7 |
| Stock change, utilities and industry | 1087.5 | 15.4 |
| Non-energy use | 0.0 | 0.0 |
| Other energy use (energy production) | 4 237.4 | 59.9 |
| Total demand | 7074.6 | 100.0 |
| Sector | Thousands of cubic metres | Share (%) |
|---|---|---|
| Manufacturing | 1231.8 | 28.97 |
| Marine transportation | 1538.2 | 36.17 |
| Commercial/institutional | 1013.2 | 23.83 |
| Mining and oil and gas extraction | 246.0 | 5.79 |
| Public administration | 100.3 | 2.36 |
| Agriculture | 76.2 | 1.79 |
| Forestry, logging, and support | 26.7 | 0.63 |
| Construction | 3.0 | 0.07 |
| ResidentialFootnote Appendix C Table C-3[b] | 16.9 | 0.40 |
| Total | 4252.3 | 100 |
| Year | Average spill volume (litres) | Maxi-mum single spill volume (litres) | Median spill volume (litres) | Number of spills reported | % of spills with unknown volume |
Total known volume spilled (litres) |
Extra-polated total volume spilledFootnote Appendix C Table C-4 [a] (litres) |
|---|---|---|---|---|---|---|---|
| 2009 | 12 592 | 98 000 | 636 | 16 | 43.8 | 113 330 | 162 834 |
| 2008 | 21 101 | 196 000 | 75 | 15 | 26.7 | 232 115 | 260 404 |
| 2007 | 27 000 | 222 460 | 200 | 27 | 22.2 | 566 995 | 609 428 |
| 2006 | 1 197 | 15 000 | 261 | 32 | 25 | 28 726 | 85 303 |
| 2005Footnote Appendix C Table C-4[b] | 6 351 | 127 184 | 227 | 52 | 36.5 | 209 599 | 343 969 |
| 2004 | 7 523 | 98 000 | 182 | 39 | 30.8 | 203 131 | 287 997 |
| 2003 | 4 230 | 79 490 | 132 | 43 | 34.9 | 118 438 | 224 520 |
| 2002 | 2 325 | 60 000 | 227 | 58 | 27.6 | 97 662 | 210 815 |
| 2001 | 3 182 | 65 000 | 216 | 32 | 18.8 | 82 744 | 125 177 |
| 2000 | 2 083 | 27 822 | 95 | 25 | 28.0 | 37 491 | 86 995 |
| - | - | - | - | - | Total volume spilled | 1 690 232 | 2 397 441 |
| Province | 2000 | 2001 | 2002 | 2003 | 2004 |
|---|---|---|---|---|---|
| Alberta | NA | NA | NA | NA | NA |
| British Columbia | 20 | 4 396 | 4 782 | 3 951 | 15 |
| Ontario | NA | 65 000 | 900 | 2 270 | 35 000 |
| Quebec | 2 520 | 3 370 | 62 155 | 19 970 | 160 351 |
| New Brunswick | 5 784 | 5 700 | 19 939 | 9 165 | 792 |
| Nova Scotia | 28 438 | 3 528 | 3 484 | 345 | 105 |
| Prince Edward Island | NA | 14 | 2 | 568 | NA |
| Newfoundland and Labrador | 729 | 736 | 6 430 | 82 169 | 2 868 |
| Nunavut | NA | NA | NA | NA | NA |
| Northwest Territories | NA | NA | NA | NA | 4000 |
| YearlyFootnote Appendix C Table C-5 [b]total | 37 491 | 82 744 | 15 598 | 16 299 | 203 131 |
| Province | 2005 | 2006 | 2007 | 2008 | 2009 | Total |
|---|---|---|---|---|---|---|
| Alberta | NAFootnote Appendix C Table C-5 [a] | NA | NA | NA | NA | NA |
| British Columbia | 8 259 | 76 | NA | NA | NA | 21 499 |
| Ontario | 25 185 | 1 200 | NA | NA | 5 200 | 134 755 |
| Quebec | 1 277 | 16 552 | 433 728 | 223 449 | NA | 923 372 |
| New Brunswick | 15 717 | 733 | 89 | 8 586 | 2 293 | 68 798 |
| Nova Scotia | 141 171 | 5 684 | 129 273 | 81 | 98 836 | 410 915 |
| Prince Edward Island | 5000 | NA | 1 095 | NA | NA | 6 678 |
| Newfoundland and Labrador | 12 991 | 4 182 | 2 787 | NA | 7001 | 119 893 |
| Nunavut | NA | 300 | NA | NA | NA | 300 |
| Northwest Territories | NA | NA | NA | NA | NA | 4 000 |
| Yearly total[b] | 209 600 | 28 727 | 566 972 | 232 116 | 113 330 | - |
| Air | Land | Freshwater | Saltwater | Total | |
|---|---|---|---|---|---|
| 2000 | 0 | 10 | 1 | 8 | 19 |
| 2001 | 1 | 12 | 4 | 11 | 27 |
| 2002 | 1 | 21 | 6 | 20 | 47 |
| 2003 | 1 | 15 | 7 | 12 | 34 |
| 2004 | 0 | 10 | 7 | 15 | 32 |
| 2005 | 0 | 22 | 10 | 17 | 49 |
| 2006 | 0 | 21 | 5 | 7 | 33 |
| 2007 | 0 | 9 | 8 | 7 | 24 |
| 2008 | 0 | 7 | 4 | 5 | 16 |
| 2009 | 1 | 4 | 3 | 6 | 13 |
| Total | 4 | 131 | 55 | 108 | - |
| Source | Total number of releases | Total volume of releases (litres) | Proportion of volume | Average release (litres) |
|---|---|---|---|---|
| Other watercraft | 43 | 416 759 | 0.25 | 14 371 |
| Pipeline | 13 | 333 431 | 0.20 | 33 343 |
| Marine tanker | 9 | 323 523 | 0.19 | 40 440 |
| Other | 46 | 156 374 | 0.09 | 4 739 |
| Other industrial plant | 44 | 133 540 | 0.08 | 3 257 |
| Marine terminal | 16 | 132 093 | 0.08 | 12 008 |
| Train | 11 | 61 304 | 0.04 | 10 217 |
| Tank truck | 21 | 37 431 | 0.02 | 2 202 |
| Refinery | 23 | 31 904 | 0.02 | 1 679 |
| Other storage facilities | 22 | 28 945 | 0.02 | 1 809 |
| Unknown | 36 | 9 294 | 0.01 | 774 |
| Storage depot | 7 | 6 550 | 0.00 | 936 |
| Transport truck | 5 | 5 150 | 0.00 | 1 030 |
| Barge | 8 | 5 018 | 0.00 | 1 004 |
| Bulk carrier | 12 | 3 805 | 0.00 | 951 |
| Chemical plant | 2 | 2 270 | 0.00 | 2 270 |
| Electrical equipment | 7 | 1 274 | 0.00 | 182 |
| Other motor vehicle | 6 | 1 129 | 0.00 | 282 |
| Production field | 4 | 418 | 0.00 | 139 |
| Migration | 2 | 20 | 0.00 | 20 |
| Municipal sewer | 1 | 0 | 0.00 | 0 |
| Service station | 1 | 0 | 0.00 | 0 |
| Aircraft | 0 | 0 | 0.00 | 0 |
| Municipal sewage treatment plant | 0 | 0 | 0.00 | 0 |
| Total | 339 | 1 690 232 | 1.00 | 7 072 |
| Cause | Total number of releases | Total volume of releases (litres) | Proportion of volume | Average release (litres) |
|---|---|---|---|---|
| Pipe leak | 74 | 644 515 | 0.38 | 10 742 |
| Unknown | 72 | 414 993 | 0.25 | 11 216 |
| Sinking | 5 | 222 860 | 0.13 | 111 430 |
| Other | 47 | 141 964 | 0.08 | 4 302 |
| Grounding | 7 | 98 980 | 0.06 | 32 993 |
| Overflow | 35 | 61 692 | 0.04 | 2 056 |
| Above-ground tank leak | 19 | 51 597 | 0.03 | 3 440 |
| Valve, fitting leak | 23 | 16 600 | 0.01 | 755 |
| Container leak | 21 | 11 267 | 0.01 | 751 |
| Discharge | 18 | 10 174 | 0.01 | 1 130 |
| Overturn | 6 | 6 637 | 0.00 | 1 659 |
| Process upset | 3 | 4 928 | 0.00 | 1 643 |
| Underground tank leak | 2 | 2 880 | 0.00 | 2 880 |
| Well blowout | 2 | 500 | 0.00 | 250 |
| Cooling system leak | 2 | 443 | 0.00 | 221 |
| Derailment | 3 | 200 | 0.00 | 200 |
| Total | 339 | 1 690 232 | 1.00 | 7072 |
| Reason | Total number of releases | Total volume of releases (litres) | Proportion of volume | Average release (litres) |
|---|---|---|---|---|
| Unknown | 119 | 721 969 | 0.43 | 10 617 |
| Material failure | 42 | 270 403 | 0.16 | 7 726 |
| Human error | 56 | 263 605 | 0.16 | 5 380 |
| Other | 29 | 196 316 | 0.12 | 10 332 |
| Fire, explosion | 1 | 98 000 | 0.06 | 98 000 |
| Equipment failure | 65 | 77 178 | 0.05 | 1 642 |
| Negligence | 3 | 35 000 | 0.02 | 35 000 |
| Gasket, joint | 11 | 19 011 | 0.01 | 1 728 |
| Damage by equipment | 4 | 5 520 | 0.00 | 1 840 |
| Power failure | 2 | 2 270 | 0.00 | 2 270 |
| Corrosion | 2 | 569 | 0.00 | 569 |
| Weld, seam failure | 1 | 190 | 0.00 | 190 |
| Intent | 2 | 182 | 0.00 | 182 |
| Migration | 2 | 20 | 0.00 | 20 |
| Overstress | 0 | 0 | 0.00 | 0 |
| Total | 339 | 1 690 232 | 1.00 | 7 072 |
Appendix D: Environmental Fate Processes Affecting HFOs
| Component | 0% weathered | 2.5% weathered |
|---|---|---|
| Alkanes (saturates) | 42.5 | 38.8 |
| Aromatics | 29.0 | 26.9 |
| Resins | 15.5 | 16.6 |
| Asphaltenes | 13.0 | 17.7 |
| Waxes | 2.5 | 2.7 |
| Volatile Organic Compound | 0% weathered | 2.5% weathered |
|---|---|---|
| Benzene | 40 | 0 |
| Toluene | 136 | 0 |
| Ethylbenzene | 58 | 0 |
| Xylenes | 396 | 0 |
| C3-benzenes | 940 | 50 |
| Total BTEx | 630 | 0 |
| Total BTEx and C3-benzenes | 1570 | 50 |
Appendix E: Persistence and Bioaccumulation
| # of carbons | C12 | C13 | C14 | C15 | C18 | C20 | C22 | C30 | C50 |
|---|---|---|---|---|---|---|---|---|---|
| n-alkane | n/a | n/a | n/a | - | - | - | n/a | - | - |
| i-alkane | - | - | n/a | - | n/a | - | n/a | S,W,Sd | - |
| monocyclo-alkane | - | n/a | n/a | - | n/a | - | n/a | Sd | S,W,Sd |
| dicyclo-alkane | Sd | n/a | n/a | S,W,Sd | n/a | S,W,Sd | n/a | S,W,Sd | S,W,Sd |
| Polycyclo-alkane | n/a | n/a | Sd | n/a | S,W,Sd | n/a | S,W,Sd | n/a | n/a |
| mono-aromatic | S,W,Sd | n/a | n/a | Sd | n/a | - | n/a | Sd | Sd |
| Cycloalkane mono-aromatic | S,W,Sd | n/a | n/a | S,W,Sd | n/a | S,W,Sd | n/a | n/a | n/a |
| diaromatic | S,W,Sd | n/a | n/a | S,W,Sd | n/a | S,W,Sd | n/a | S,W,Sd | S,W,Sd |
| Cycloalkane diaromatic | S,W,Sd | A | n/a | - | n/a | - | n/a | n/a | n/a |
| 3-ring polyaromatic | A | n/a | A, S,W,Sd | - | n/a | - | n/a | S,W,Sd | S,W,Sd |
| 4-ring polyaromatic | n/a | n/a | n/a | n/a | A, S,W,Sd | S,W,Sd | n/a | n/a | n/a |
| 5-ring polyaromatic | n/a | n/a | n/a | n/a | n/a | A, S,W,Sd | n/a | S,W,Sd | n/a |
| 6-ring polyaromatic | n/a | n/a | n/a | n/a | n/a | n/a | A, S,W,Sd | n/a | n/a |
| # of carbonsFootnote Appendix E Table E-2[a] | C12 | C13 | C14 | C15 | C18 | C20 | C22 | C25 |
|---|---|---|---|---|---|---|---|---|
| n-alkane | - | - | - | - | - | - | n/a | n/a |
| i-alkane | - | B | n/a | B | n/a | n/a | n/a | n/a |
| mono-cycloalkane | B | n/a | n/a | B | n/a | n/a | n/a | n/a |
| dicycloalkane | B | - | n/a | B | n/a | n/a | n/a | n/a |
| poly-cycloalkane | n/a | n/a | B | n/a | - | n/a | B | n/a |
| monoaromatic | - | n/a | n/a | B | n/a | n/a | n/a | n/a |
| Cycloalkane monoaromatic | - | n/a | n/a | B | n/a | B | n/a | n/a |
| Diaromatic | B | B | - | - | n/a | n/a | n/a | n/a |
| Cycloalkane diaromatic | - | - | - | - | n/a | B | n/a | n/a |
| 3-ring polyaromatic | - | n/a | B | - | n/a | B | n/a | n/a |
| 4-ring poly-aromatic | n/a | n/a | n/a | B | B | B | n/a | n/a |
| 5-ring poly-aromatic | n/a | n/a | n/a | n/a | n/a | B | B | n/a |
| 6-ring poly-aromatic | n/a | n/a | n/a | n/a | n/a | n/a | B | n/a |
Appendix F: Ecotoxicological Information
Table F-1a. Aquatic toxicity of Fuel Oil No. 6
| Test organism (common name) | Type of test | Comment | Value (mg/L) | Reference |
|---|---|---|---|---|
| Oncorhynchus kisutch (coho salmon) |
96-hr acute LC50 | OWD | 4800 | Hebert and Kussat 1972 |
| Oncorhynchus kisutch (coho salmon) |
96-hr acute LC50 | OWD | greater than 10 000 | Hebert and Kussat 1972 |
| Oncorhynchus kisutch (coho salmon) |
96-hr acute LC50 | OWD | 7500 | Hebert and Kussat 1972 |
| Alosa sapidissma (American shad) | 48-hr acute LC50 | Not reported | 2417 | Tagatz 1961 |
| Leptocottus armatus (staghorn sculpin) | 96-hr acute LC50 | OWD | 780 | Hebert and Kussat 1972 |
| Leptocottus armatus (staghorn sculpin) | 96-hr acute LC50 | OWD | 5600 | Hebert and Kussat 1972 |
| Leptocottus armatus (staghorn sculpin) | 96-hr acute LC50 | OWD | 3400 | Hebert and Kussat 1972 |
| Salmo salar (Atlantic salmon) |
96-hr acute LC50 | OWD | greater than 10 000 | Sprague and Carson 1970 |
| Pseudopleuronectes americanus (winter flounder) |
96-hr acute LC50 | OWD | greater than 10 000 | Sprague and Carson 1970 |
| Fundulus similis (longnose killifish) | 24-hr acute LC50 | WSFFootnote Appendix F Table F-1a[a] | 3.8 | Anderson et al. 1974 |
| Fundulus similis (longnose killifish) | 48-hr acute LC50 | WSF[a] | 2.27 | Anderson et al. 1974 |
| Fundulus similis (longnose killifish) | 96-hr acute LC50 | WSF[a] | 1.69 | Anderson et al. 1974 |
| Menidia menidia (Atlantic silverside) | 96-hr acute LC50 | Not reported | 130 | Hollister et al. 1980 |
| Cyprinodon variegates (sheepshead minnow) | 96-hr acute LC50 | WSF[a] | 4.7 | Anderson et al. 1974 |
| Cyprinodon variegatus (sheepshead minnow) | 96-hr acute LC50 | WSF[a] | 4.4 | Anderson et al. 1974 |
| Cyprinodon variegatus (sheepshead minnow) | 96-hr acute LC50 | WSF[a] | 3.1 | Anderson et al. 1974 |
| Menidia beryllina (inland silverside) | 24-hr acute LC50 | WSF[a] | 3.6 | Anderson et al. 1974 |
| Menidia beryllina (inland silverside) | 48-hr acute LC50 | WSF[a] | 2.7 | Anderson et al. 1974 |
| Menidia beryllina (inland silverside) | 96-hr acute LC50 | WSF[a] | 1.9 | Anderson et al. 1974 |
| Lepomis macrochirus (bluegill) | 96-hr acute LC50 | OWD | greater than 10 000 | Mobil 1987a |
| Test organism (common name) | Type of test | Comment | Value (mg/L) | Reference |
|---|---|---|---|---|
| Daphnia magna (water flea) | 48-hr acute EC50 (immobilization) | WSF | 4.14 | MacLean and Doe 1989 |
| Daphnia magna (water flea) |
48-hr acute LC50 | WSF | greater than 4.45 | MacLean and Doe 1989 |
| Daphnia magna (water flea) |
48-hr acute EL50 | OWD | greater than 10 000 | Mobil 1987b |
| Artemia salina (brine shrimp) |
48-hr acute EC50 (immobilization) | WSF | greater than 2.29 | MacLean and Doe 1989 |
| Artemia salina (brine shrimp) |
48-hr acute LC50 | WSF | greater than 2.29 | MacLean and Doe 1989 |
| Acartia tonsa (copepod) |
96-hr acute LC50 | Not reported | 5.1 | Hollister et al. 1980 |
| Paleomonetes pugio (grass shrimp) |
24-hr acute LD50 | WSF[a] | 3.2 | Anderson et al. 1974 |
| Paleomonetes pugio (grass shrimp) |
48-hr acute LD50 | WSF[a] | 2.8 | Anderson et al. 1974 |
| Paleomonetes pugio (grass shrimp) |
96-hr acute LD50 | WSF[a] | 2.6 | Anderson et al. 1974 |
| Paleomonetes pugio (grass shrimp) |
96-hr acute LC50 | WSF-1:9, 20-hr mix, serial dilutions, ppm dissolved total HC by IR | 2.6 3.1 2.2 |
Tatem et al. 1978 |
| Penaeus aztecus (postlarvae) (brown shrimp) |
24-hr acute LC50 | WSF[a] | 3.8 | Anderson et al. 1974 |
| Penaeus aztecus (postlarvae) (brown shrimp) |
48-hr acute LC50 | WSF[a] | 3.5 | Anderson et al. 1974 |
| Penaeus aztecus (postlarvae) (brown shrimp) |
96-hr acute LC50 | WSF[a] | 1.9 | Anderson et al. 1974 |
| Limulus polyphemus (horseshoe crabs [juvenile]) |
7 days (Increased mortality and delayed moult) |
2.25 | Strobel and Brenowitz 1981 | |
| Mercenaria mercenaria (horseshoe crabs [juvenile]) |
48-hr acute LC50 | WSF concentration = 25.2 ± 1.7 ppm | 1.0 (0.7–1.6) ppm |
Byrne and Calder 1977 |
| Mercenaria mercenaria (horseshoe crabs [juvenile]) | 48-hr acute LC50 | WSF concentration = 25.2 ± 1.7 ppm | 3.2 (2.3–4.5) ppm |
Byrne and Calder 1977 |
| Mercenaria mercenaria (horseshoe crabs [juvenile]) | 6-day LC50 | WSF concentration = 25.2 ± 1.7 ppm | 1.8 (1.0–2.6) ppm |
Byrne and Calder 1977 |
| Mercenaria mercenaria (horseshoe crabs [juvenile]) | 10-day LC50 | WSF concentration = 25.2 ± 1.7 ppm | 1.6 (1.1–2.2) ppm |
Byrne and Calder 1977 |
| Mercenaria mercenaria (horseshoe crabs [juvenile]) | 6-day growth test EC50 | WSF concentration = 25.2 ± 1.7 ppm | 1.9 (1.6–2.1) ppm |
Byrne and Calder 1977 |
| Mercenaria mercenaria (horseshoe crabs [juvenile]) | 10-day growth test EC50 | WSF concentration = 25.2 ± 1.7 ppm | 1.0 (0.49–2.04) ppm |
Byrne and Calder 1977 |
| Neanthes arenaceodentata (polychaete marine worm) | 96-hr acute LC50 | Not given | 3.6 | Neff and Anderson 1981 |
| Neanthes arenaceodentata (polychaete marine worm) | 24-hr acute LC50 | WSF | greater than 6.3 | Rossi et al. 1976 |
| Neanthes arenaceodentata (polychaete marine worm) | 48-hr acute LC50 | WSF | 4.6 | Rossi et al. 1976 |
| Neanthes arenaceodentata (polychaete marine worm) | 96-hr acute LC50 | WSF | 3.6 | Rossi et al. 1976 |
| Capitella capitata (marine worm) |
24-hr acute LC50 | WSF | greater than 6.3 | Rossi et al. 1976 |
| Capitella capitata (marine worm) |
48-hr acute LC50 | WSF | 1.1 | Rossi et al. 1976 |
| Capitella capitata (marine worm) |
96-hr acute LC50 | WSF | 0.9 | Rossi et al. 1976 |
| Capitella capitata (marine worm) |
96-hr acute LC50 | Not reported | 0.9 | Neff and Anderson 1981 |
| Mysidopsis almyra (mysid shrimp) | 24-hr acute LC50 | WSF | 6.3 | Anderson et al. 1974 |
| Test organism (common name) | Type of test | Comment | Value (mg/L) | Reference |
|---|---|---|---|---|
| Skeletonema costatum (diatom) |
96-hr acute EC50 | Not given | 160 | Hollister et al. 1980 |
| Pseudokirchneriella subcapitata (Selenastrum capricornutum) (green alga) |
EC50 | WSF-1:8, 16-hour mix, serial dilutions | No inhibition – 100% WSF Stimulation – 0.1% WSF |
Giddings et al. 1980 |
| (Green alga) | 96-hr acute EC50 | Material heated, spread in container, water overlay | greater than 5000 | Mobil 1987c |
| Microsystus aeruginosa (blue-green alga) |
EC50 | WSF-1:8, 16-hour mix, serial dilutions | No inhibition – 100% WSF Stimulation – 0.1% WSF |
Giddings et al. 1980 |
| Test organism / common name | Residual Fuel Oil type | Type of test / endpoint | Comment | Value (mg/L) |
Reference |
|---|---|---|---|---|---|
| Oncorhynchus mykiss rainbow trout |
Heavy | 96-hr acute LL50 | WAF; semistatic | 100–1000 | Shell 1997a |
| Oncorhynchus mykiss rainbow trout |
Light | 96-hr acute LL50 | WAF | More than 1000 | Shell 1997b |
| Daphnia magna water flea |
Heavy | 48-hr acute EL50 (immobilization) NOEL |
WAF; static | 220–460 100 (10% immobilization) |
Shell 1997c |
| Daphnia magna water flea |
Light | 48-hr acute EL50 (immobilization) |
WAF | More than 1000 | Shell 1997d |
| Raphidocelis subcapitata algae |
Heavy | 96-hr acute EL50 (growth rate) |
WAF | 30–100 | Shell 1997e |
| Raphidocelis subcapitata algae |
Light | 72-hr acute EL50 (growth rate) |
WAF | 100–300 | Shell 1997f |
| Fuel Oil No. | Oral LD50, rat (mg/kg) | Reference |
|---|---|---|
| Fuel Oil No. 6, API 78-6 | greater than 25 000 | API 1980b |
| Fuel Oil No. 6, API 78-7 | greater than 25 000 | API 1980a |
| Fuel Oil No. 6, API 78-8 | greater than 24 700 | API 1980c |
| Fuel Oil No. 6, API 79-2 | 5 130 | API 1980d |
| Spill size (barrels) | Loading/unloading | Transport |
|---|---|---|
| 1–49 | 60 | 5 750 |
| 50–999 | 150 | 6 250 |
| 1000–9999 | 300 | 9 600 |
| 10 000–99 999 | 2 200 | 17 350 |
| 100 000–199 999 | 32 500 | 49 500 |
| greater than 200 000 | 35 000 | 74 100 |
Appendix G: Summary of Health Effects Information for Fuel Oil No. 4, Fuel Oil No. 6, Residual Fuel Oil and Related HFOs
| Endpoints | CAS RNFootnote Appendix G Table G-1[a] | Effect levelsFootnote Appendix G Table G-1[b]/results |
|---|---|---|
| Acute health effects | 68476-33-5 | Inhalation LC50 (rat) = 4100 mg/m3 (male and female). Non-lethal effects included laboured breathing, gasping and reduced activity (Bio/Dynamics Inc. 1987). |
| Acute health effects | 64742-90-1 | Lowest inhalation LC50 (rat) = greater than 3700 mg/m3 (male and female) (U.S. EPA 2005). |
| Acute health effects | 68553-00-4 | Oral LD50s (rat) = 5130, greater than 24 700, greater than 25 000 and greater than 25 000 mg/kg-bw (5.13, greater than 25, greater than 25 and greater than 25 mL/kg) for samples API 79-2, 78-8, 78-7 and 78-6, respectively (male and female) (CONCAWE 1998; API 2004; European Commission c2000b). |
| Acute health effects | 64741-62-4 | Lowest oral LD50 (rat) = greater than 2000 mg/kg-bw (male and female) (CONCAWE 1998; European Commission c2000b). |
| Acute health effects | 64741-62-4 64741-45-3 64741-57-7 64741-81-7 64742-90-1 |
Other oral LD50s (rat) = 4320–5898 mg/kg-bw for 5 CAS RNs tested (female and/or male) (CONCAWE 1998; API 2004; European Commission c2000b; U.S. EPA 2005). |
| Acute health effects | 68476-31-3 | Dermal LD50 (mouse) = greater than 40 000 mg/kg-bw (male and female) (CONCAWE 1996). |
| Acute health effects | 68553-00-4 | Dermal LD50s (rabbit) = greater than 5350, greater than 5000, greater than 5000, greater than 4940 mg/kg-bw (greater than 5 mL/kg-bw) for samples API 79-2, 78-8, 78-7, 78-6, respectively (male and female) (CONCAWE 1998; API 2004; European Commission c2000b). |
| Acute health effects | 64741-45-3 64741-57-7 64741-62-4 64741-81-7 |
Lowest dermal LD50 (rabbit) = greater than 2000 mg/kg-bw for 4 CAS RNs tested (male and female) (API 2004; CONCAWE 1998; European Commission c2000b). |
| Acute health effects | 64742-90-1 | Other dermal LD50 (rabbit) = greater than 3160 mg/kg-bw (male and female) (European Commission c2000b). |
| Acute health effects | 64741-62-4 | Other dermal LD50 (rat) = greater than 2000 mg/kg-bw (male and female) (European Commission c2000b). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 68476-31-3 | Inhalation LOAEC = less than or equal to 300 mg/m3for decreased body weight gain. Male and female rats were exposed for 90 days to 50 or 300 mg/m3 test substance. Reduced body weight gain was observed at an unspecified concentration. Nephropathy was also observed in males, but was not considered by the authors to be relevant to humans (Cowan and Jenkins 1981). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 64742-90-1 | Other inhalation study: Male and female Fischer 344 rats (5 animals per sex per concentration) were exposed to 540 or 2000 mg/m3 test substance for 6 hours per day for 9 days. Concentration- and time-related decreases in body weight (greater effect in males), as well as concentration-related increases in hair loss, nasal discharge, discharge from the eyes, eyes closed and perianal soiling, were observed. Yellow discolouration of the lungs and hyperplasia of the pulmonary alveolar macrophages were also observed at all concentrations. Increased liver weight was observed in females at 540 mg/m3 and in both sexes at 2000 mg/m3. Increased lung (females), decreased spleen (male and female) and decreased heart (male) weights were also observed at the highest concentration (Gordon 1983). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 68476-31-3 | Dermal study: Doses of 2000, 4000, 8000, 20 000 or 40 000 mg/kg-bw per day were applied to the clipped dorsal interscapular skin of male and female B6C3F1 mice (5 animals per sex per dose) for 14 consecutive days. Skin lesions characterized by moderate acanthosis, perakeratosis and hyperkeratosis, accompanied by moderate mixed cellular inflammatory infiltrate within the upper dermis were observed at all doses. Mortality of all mice occurred between days 7 and 12 at the highest dose (NTP 1986). Dermal study: Doses of 425, 818 or 1625 mg/kg-bw per day (11.9, 22.9 or 45.5 mg per day)Footnote Appendix G Table G-1[c],Footnote Appendix G Table G-1 [d]were applied to male and female C3Hf mice, 3 days per week for 40 weeks. Decreased body weight (4–21%), increased spleen weight (male and female), increased relative kidney weight (females) and decreased relative kidney weight (males) were observed at 818 mg/kg-bw per day (Schultz et al. 1981). Dermal study: Doses of 694 or 1111 mg/kg-bw per day (50 µL of 50% w/v diluted in cyclohexane or 50 µL neat)[c],Footnote Appendix G Table G-1 [e],Footnote Appendix G Table G-1 [f] were applied to the clipped interscapular skin of male and female C3Hf/Bd mice (15 animals per sex per dose), 3 times per week for 60 weeks. Hyperkeratosis, alopecia and ulceration at the application site, as well as increased daily water consumption (possibly due to increased water loss) and increased urine output, were observed at all doses. An increased incidence of macroscopic renal lesions (affected kidneys were shrunken, pale and nodular) were observed in females at the highest dose (Easley et al. 1982). Dermal study: Doses of 250, 500, 1000 and 2000 mg/kg-bw per day (diluted in 0.2 mL of acetone) or 4000 mg/kg-bw per day (neat) were applied to the shaved interscapular skin of male and female B6C3F1 mice (10 animals per sex per dose), 5 days per week for 13 weeks. Decreased body weight (8–13%) in males was observed at all doses. An increased incidence of dermatosis was observed, with mild dermatitis occurring at the highest dose. Extramedullary haematopoiesis in the spleen and karyomegaly in the liver were observed at an unspecified dose (NTP 1986). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 68553-00-4 | Dermal study: A dose of 8000 mg/kg-bw per day (8 mL/kg per day)Footnote Appendix G Table G-1 [g],Footnote Appendix G Table G-1 [h] was applied to male and female New Zealand white rabbits (4 animals per sex) for 5 days, followed by 2 days of rest, followed by 5 more days of exposure. Severe dermal irritation and injury (acanthosis, chronic inflammation, crusting, dermal congestion, dermal oedema and hyperkeratosis) were observed at the application site. Mortality (25%) occurred after a single exposure. Reduced food consumption, slight epithelial hyperplasia of the urinary bladder mucosa (4/8 rabbits), slight centrilobular vacuolar degeneration in the liver (3/8 rabbits) and severe multifocal liver necrosis (7/8 rabbits) were observed (API 1980a, 1980b, 1980c). Dermal study: Doses of 1070, 2140 or 2675 mg/kg-bw per day (1, 2 or 2.5 mL/kg per day)[g],[h]were applied to male and female Sprague-Dawley rabbits (4 animals per sex per dose) for 5 days, followed by 2 days of rest, followed by 5 more days of exposure. Significant skin irritation (acanthosis, acute and chronic inflammation, crusting, deep pyoderma, dermal congestion and oedema, hyperkeratosis and epidermal necrolysis) was observed at the treatment site at all doses. Multifocal necrosis and centrilobular vacuolar degeneration of the liver were also observed at all doses (API 1980d). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 68476-33-5 | Dermal study: Doses of 496, 992 or 2480 mg/kg-bw per day (0.5, 1.0 or 2.5 mL/kg per day) were applied to male and female Sprague-Dawley rats (10 animals per sex per dose), 5 days per week for 28 days. Minimal reversible dermal irritation was observed at all dose levels. Hyperkeratosis (minimal severity) was observed at the application site at the highest dose. Significant increase in relative liver weight was observed for both sexes at all dose levels. No other substance-related systemic effects were observed (UBTL 1987). Dermal study: Doses of 496, 992 or 1984 mg/kg-bw per day (0.5, 1.0 or 2.0 mL/kg per day)[h],Footnote Appendix G Table G-1 [i] were applied to male and female Sprague-Dawley rats (10 animals per sex per dose), 5 days per week for 4 weeks. Mild histopathologic dermal lesions (acanthosis and hyperkeratosis) were observed at 1984 mg/kg-bw in both sexes. Possible dose-related decrease in body weight gain was observed in males (decrease at 992 mg/kg-bw and statistically significant decrease at 1984 mg/kg-bw). Test substance-related anemia was observed, as indicated by increased absolute and relative spleen weights in combination with the absence of abnormal pathological spleen appearances, as well as decreased red blood cell indices (erythrocyte count, hematocrit (%) and hemoglobin levels), at all three dose levels in both sexes (UBTL 1988). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 64741-62-4 | Dermal LOAEL (short-term) = 1 mg/kg-bw per day for dose-related decreases in maternal body weight gain, body weight, food consumption and gravid uterine weight, as well as the occurrence of red vaginal exudates. Doses of 0.05, 1.0, 10, 50 or 250 mg/kg-bw per day were applied to the clipped skin of pregnant CD rats from gestational days 0 to 19 (Hoberman et al. 1995). Other dermal study (short-term): Doses of 8, 30, 125 or 500 mg/kg-bw per day or 4, 30, 125 or 500 mg/kg-bw per day were applied to the shaved backs of pregnant Sprague-Dawley rats (15 animals per dose) from gestational days 0 to 19 (4 mg/kg-bw per day dose given as 8 mg/kg-bw every other day). Aberrant serum chemistry, decreased body weight gain and food consumption, as well as vaginal discharge, were observed at 8 mg/kg-bw per day (applied every other day) (Mobil 1990; Feuston et al. 1997). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 64741-81-7 | Other dermal study (short-term):Doses of 8, 30, 125 or 250 mg/kg-bw per day were applied to the shaved backs of pregnant Sprague-Dawley rats (15 animals per dose) from gestational days 0 to 19. At 8 mg/kg-bw per day, decreased thymus weights (relative and absolute), increased liver weights (relative) and skin irritation (dose-related) were observed. Altered haematology parameters and aberrant serum chemistry occurred at an unspecified dose, as well as dose-related skin irritation. Red vaginal discharge, paleness and emaciation were observed at 30 mg/kg-bw per day. Moribundity was observed at 250 mg/kg-bw per day (Mobil 1994a). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 64741-62-4 | Dermal LOAEL (subchronic) = 8 mg/kg-bw per day for increased relative liver weight (male and female rats) and increased absolute liver weight (female). Doses of 8, 30, 125, 500 or 2000 mg/kg-bw per day were applied to the shorn backs of Sprague-Dawley rats, 5 times per week for 13 weeks. Increased mortality, decreased body weights, decreased thymus weight and aberrant serum chemistry and haematology were also observed at unspecified doses (Feuston et al. 1994). Dermal LOAEL (subchronic) = 8 mg/kg-bw per day for a significant reduction in platelet count. Doses of 8, 30, 125 or 500 mg/kg-bw per day were applied to the shaved backs of male and female Sprague-Dawley rats (10 animals per sex per dose), 5 times per week for 13 weeks. Increased liver weight was observed for males and females at 30 mg/kg-bw per day and 125 mg/kg-bw per day, respectively. At 30 mg/kg-bw per day (male) and 125 mg/kg-bw per day (female), dose-related reductions in red blood cell, haemoglobin, haematocrit and platelet counts, a dose-related decrease in thymus weight, and increased mortality (20% males and 80% females) were also observed. At 125 mg/kg-bw per day, both sexes exhibited decreased body weight gain. All male and female rats died at 125 and 500 mg/kg-bw per day, respectively (Mobil 1988; Feuston et al. 1997). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 64741-81-7 | Dermal LOAEL (subchronic) = 8 mg/kg-bw per day for moderate skin irritation (dose-related). Doses of 8, 30 or 125 mg/ kg-bw per day were applied to the shaved backs of male and female Sprague-Dawley rats (10 animals per sex per dose), 5 times per week for 13 weeks. Altered haematology features and decreased thymus weight (relative and absolute), as well as altered serum chemistry were observed at 30 mg/kg-bw per day. Decreased body weight gain (males), increased liver weight (relative and absolute) and a decreased number of lymphoid cells in the thymus were observed at 125 mg/kg-bw per day (Mobil 1994b). |
| Short-term, subchronic and and non-cancer chronic repeated-exposure health effects | 64741-62-4 | Oral LOAEL = greater than or equal to 125 mg/kg for maternal toxicity. A single dose of 2000 mg/kg on either GD 11, 12, 13, 14 or 15 (to profile effects as a function of gestation day) or single doses of 125, 500 or 2000 mg/kg on GD 12 (to profile effects as a function of dose) were administered to pregnant Sprague-Dawley rats. (1) General observations (greater than or equal to 500 mg/kg): Red vaginal discharge, perineal staining and decreased stool. (2) Effects versus gestation day (2000 mg/kg): Decreased body weight gain and thymus weight (regardless of exposure day). (3) Effects versus dose (GD 12): Dose-related decrease in body weight gain and thymus weight (Feuston and Mackerer 1996). |
| Carcinogenicity | 68476-31-3 | Chronic dermal studies Doses of 0, 250 or 500 mg/kg-bw (100 µL applied; test substance diluted in acetone) were applied to the clipped dorsal interscapular skin of B6C3F1 mice (49-50 animals per sex per dose) 5 times per week for 103 weeks. High-dose mice were sacrificed early due to severe irritation at the application site. Skin tumour incidence in male mice (squamous cell papillomas or carcinomas combined) occurred at the application site at the high dose (0/49, 0/49 and 3/49 of mice developed tumours, respectively). Incidence in female mice (squamous cell carcinomas only) at the application site was (0/50, 1/45 and 2/48, respectively). Liver tumour incidence in male mice (hepatocellular adenomas or carcinomas combined) was 9/50, 17/48 and 14/49, respectively. Liver tumour incidence in female mice (hepatocellular adenomas and carcinomas combined) were 4/50, 4/45 and 5/50 (NTP 1986). Doses of 0, 694 or 1111 mg/kg-bw (50 µL at 50% w/v[c],[e]or 100%[c],[f], respectively) were applied to the clipped interscapular skin of C3Hf/Bd mice (15 animals per sex per dose) 3 times per week for 60 weeks. Of a larger combined group (groups of mice that received 1 of 5 other test substances), 34/360 developed skin tumours. A breakdown of the number of mice that received 68476-31-3 and developed tumours was not provided. Exposure to the negative control resulted in 1/60 mice developing skin tumours (Easley et al. 1982). |
| Carcinogenicity | 68476-33-5 | A dose of approximately 592 mg/kg-bw (25 μl)[c],[f],Footnote Appendix G Table G-1 [j] was applied to the skin of male C3H/HeJ mice (50 animals per group) 3 times per week for life. Two samples of thermally cracked residual fuel oil, as well as a blend of straight-run and Residual Fuel Oil, were tested. All three samples were concluded to be dermal carcinogens. Skin tumours developed in 16/20 and 26/50 mice for the two thermally cracked samples, with mean latency periods of 96 and 85 weeks, respectively. Skin tumours developed in 30/50 mice for the blended sample, with a mean latency period of 81 weeks. Positive and negative control substances produced expected results (Exxon Biomedical Sciences Inc. 1992). |
| Carcinogenicity | 64741-62-4 | Doses of 8.4, 16.8, 42, 83.8 or 167.6 mg/kg-bw (25 μL of catalytically cracked clarified oil at 1, 2, 5, 10 or 20% in mineral oil)[c],[f],Footnote Appendix G Table G-1 [k],Footnote Appendix G Table G-1 [l] were applied to male C3H mice (50 animals per dose) 3 times per week for life. At 1%, 9/50 exposed mice developed tumours (4 carcinomas, 5 papillomas). At 2%, 34/50 exposed mice developed tumours (30 carcinomas, 4 papillomas with a latency period of 92 weeks). At 5%, 46/50 exposed mice developed tumours (46 carcinomas with a latency period of 61 weeks). At 10%, 48/50 exposed mice developed tumours (47 carcinomas, 1 papilloma with a latency period of 45 weeks). At 20%, all (50/50) exposed mice developed tumours (50 carcinomas with a latency period of 36 weeks). Of the 610 mice tested with the negative control (highly refined mineral oil) from this study and two other similar studies conducted by the same authors, only 2 mice developed benign papillomas and none developed carcinomas (McKee et al. 1990). Initiation/promotion dermal study |
| Developmental & reproductive health effects | 64741-62-4 | Dermal reproductive LOAEL (female) = 1 mg/kg-bw per day for decreased number of live fetuses, increased incidence of resorptions, early resorptions and the percentage of dead or resorbed conceptuses per litter (these effects were dose-related and were observed at doses that were maternally toxic). Doses of 0.05, 1.0, 10, 50 or 250 mg/kg-bw per day were applied to the clipped skin of pregnant CD rats from gestational days 0 to 19. At 1 mg/kg-bw per day, an increased incidence in fetal variations associated with a decrease in fetal body weight was observed, including slight dilation of the lateral ventricles of the brain, moderate dilation of the renal pelvis, bifid thoracic vertebral centrum and decreased average number of ossified caudal vertebrae, metacarpals and hindpaw phalanges (these effects were noted to be reversible delays in development). (Hoberman et al. 1995). Dermal developmental LOAEL = 8 mg/kg-bw for fetal external abnormalities. Doses of 4, 8, 30, 125 or 250 mg/kg-bw per day were applied to the shaved backs of pregnant Sprague-Dawley rats (10 per dose) for gestational days 0–19 (the 4 mg/kg-bw dose was given as 8 mg/kg-bw every other day). At 8 mg/kg-bw per day, external abnormalities in living and dead fetuses, including cleft palate, micrognathia (shortened lower jaw) and kinked tail, were observed. An increased incidence of resorptions, decreased number of viable offspring, reduced fetal size, visceral anomalies and skeletal variations were observed at 30 mg/kg-bw per day. There were no viable fetuses at 250 mg/ kg-bw per day (Feuston et al. 1989; Mobil 1987e). Other dermal study: Doses of 4, 8, 30, 125 or 500 mg/kg-bw per day were applied to the shaved backs of pregnant Sprague-Dawley rats (15 per dose) from gestational days 0 to 19 (4 mg/kg-bw per day dose was administered as 8 mg/kg-bw every other day). At 8 mg/kg-bw per day, an increased incidence of resorptions and a decreased number of viable fetuses was observed (biologically significant). At 30 mg/kg-bw per day, a statistically significant increased incidence of resorptions was observed, as well as decreased fetal body weight. An increased incidence of fetal external, skeletal and visceral anomalies (primarily rib malformations and cleft palate) was observed at 500 mg/kg-bw per day (Mobil 1990; Feuston et al. 1997). Other dermal study: Doses of 8, 30, 125 or 500 mg/kg-bw per day were applied to the shaved backs of male Sprague-Dawley rats (10 per dose), 5 times per week for 13 weeks. Decreased sperm count after 9 weeks of exposure was observed at 500 mg/kg-bw per day (Mobil 1988; Feuston et al. 1997). Oral reproductive and developmental LOAEL = greater than or equal to 125 mg/kg for increased resorptions, decreased fetal body weight and increased incidence of skeletal malformations. Pregnant Sprague-Dawley rats were administered 2000 mg/kg on one of gestational days (GD) 11–14 (to generate a profile of teratogenic effects as a function of gestation day). Additionally, 125, 500 or 2000 mg/kg was administered on gestational day 12 (to generate a profile of teratogenic effects as a function of dose). Test samples were clarified slurry oilandsyntower bottoms. |
| Genotoxicity – in vivo | 64741-62-4 | Unscheduled DNA Synthesis Sister Chromatid Exchange |
| Genotoxicity – in vivo | 64742-90-1 | Micronuclei Induction Groups of CD Swiss mice (10 animals per sex per dose) were administered 1250, 2500 or 5000 mg/kg-bw test substance by oral gavage over 2 days. Another group (15 animals per sex) was administered a single dose of 5000 mg/kg-bw. A significant increase in micronucleated polychromatic erythrocytes was observed at greater than or equal to 1250 mg/kg-bw (males) and at 5000 mg/kg-bw (females) (Khan and Goode 1984). |
| Genotoxicity – in vitro | 68476-31-3 | Mutagenicity Test substance was negative inS. typhimurium TA98 with and without S9 metabolic activation (Schultz et al. 1981). Inhibition of Morphological Transformation |
| Genotoxicity – in vivo | 68553-00-4 | Mutagenicity Test substance was also negative in a forward mutation assay using Chlamydomonas reinhardtii (Vandermeulen and Lee 1986). Sister Chromatid Exchange Mouse Lymphoma Assay |
| Genotoxicity – in vivo | 64741-62-4 | Mouse Lymphoma Assay L5178Y cells were exposed to sample API 81-15 at concentrations ranging from 0.061–31.3 nL/mL for 4 hours, with and without S9 rat liver metabolic activation. Toxicity was noted at all levels and survival was less than 10% at concentrations above 3.9 nL/mL. Without activation, the test substance was weakly positive at the highest concentration only. With activation, the test substance induced a concentration-related increase in mutant frequency at concentrations greater than 0.977 nL/mL (API 1985c). |
| Genotoxicity – in vivo | 64741-62-4 / 64741-61-3 | Mutagenicity S. typhimurium TA98 was exposed to DMSO extracts of combined test substances at concentrations of 0.5, 1, 2.5, 5 or 10 µL/plate with S9 metabolic activation (Aroclor 1254-induced rat liver). A concentration-related increase in mutagenic potency was observed, with a mutagenicity index of 130 (Blackburn et al. 1984). Additionally, S. typhimurium TA98 was exposed to DMSO extracts (dissolved in cyclohexane) at concentrations of 0.5, 1, 1.5, 2 or 5 µL/plate with S9 metabolic activation (Aroclor 1254-induced Syrian golden hamster liver). A concentration-related increase in mutagenic potency was observed, with a mutagenic index of approximately 58 (Blackburn et al. 1986). |
| Genotoxicity – in vivo | 64742-90-1 | Unscheduled DNA Synthesis Mutagenicity |
| Genotoxicity – in vivo | 64741-62-4 | Sister Chromatid Exchange Cell Transformation |