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

Table A-1. Description of the nine groups of petroleum substances
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

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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]

Alkanes
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
Isoalkanes
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
One-ring cycloalkanes
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
Two-ring cycloalkanes
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
Polycycloalkanes
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
One-ring aromatics
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
Cycloalkane monoaromatics
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
Two-ring aromatics
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
Cycloalkane diaromatics
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
Three-ring aromatics
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
Four-ring aromatics
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.)
Five-ring PAHs
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
Six-ring aromatics
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.)
Alkanes
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
Isoalkanes
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
One-ring cycloalkanes
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
Two-ring cycloalkanes
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
Polycycloalkanes
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
One-ring aromatics
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
Cycloalkane monoaromatics
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
Two-ring aromatics
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
Cycloalkane diaromatics
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
Three-ring aromatics
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
Four-ring aromatics
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.)
Five-ring PAHs
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
Six-ring aromatics
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.)

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Appendix C: Production and Transportation of Fuel Oil No. 6, Fuel Oil No. 4 and Residual Fuel Oil

Table C-1a. Supply and disposition of HFOsFootnote Appendix C Table C-1a [a] in Canada in thousands of cubic metres, 2008 (Statistics Canada 2009)
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
Table C-1b. HFOFootnote Appendix C Table C-1b [a] production and imports available for sale in Canada in thousands of cubic metres, 2006–2008 (Environment Canada 2008, 2009, 2010)
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
Table C-1c. Production and movement of Fuel Oil No. 4, Fuel Oil No. 5 and Fuel Oil No. 6 in Canada in thousands of cubic metres, 2004–2008 (Statistics Canada 2005–2009)
Refinery production Imports Exports
2004 9154 2919 3678
2005 8670 2740 3668
2006 8146 1563 3714
2007 8617 1938 4317
2008 8258 1767 4550
Table C-2. Disposition of HFOsFootnote Appendix C Table C-2 [a] in Canada, 2008 (Statistics Canada 2010)
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
Table C-3. Sector consumption of HFOsFootnote Appendix C Table C-3 [a] in Canada, 2008 (Statistics Canada 2010)
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
C-4. Reported and extrapolated release volumes and spill numbers of Bunker C spilled in Canada, 2000–2009 (Environment Canada 2011a)
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
Table C-5. Approximate volume (litres) of Bunker C spills in Canada, 2000–2009 (Environment Canada 2011a)
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
Table C-5 cont. Approximate volume (litres) of Bunker C spills in Canada, 2000–2009 (Environment Canada 2011a)
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 -
Table C-6. Number of Bunker C spillsFootnote Appendix C Table C-6 [a] affecting air, land, freshwater and saltwater in Canada,2000–2009 (Environment Canada 2011a)
  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 -
Table C-7a. Sources of Bunker C spills in Canada, 2000–2009 (Environment Canada 2011a)
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
Table C-7b. Causes of Bunker C spills in Canada, 2000–2009 (Environment Canada 2011a)
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
Table C-7c. Reasons for Bunker C spills in Canada, 2000–2009 (Environment Canada 2011a)
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

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Appendix D: Environmental Fate Processes Affecting HFOs

Table D-1. Changes in the concentration (wt %) of Heavy Fuel Oil 6303 (Bunker C; representing Fuel Oil No. 6) components after weathering (Environment Canada 2010a)
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
Table D-2. Changes in the concentration (μg/g) of volatile organic compounds in Heavy Fuel Oil 6303 (Bunker C; representing Fuel Oil No. 6) after weathering (Environment Canada 2010)
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

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Appendix E: Persistence and Bioaccumulation

Table E-1. An analysis of persistence data for petroleum hydrocarbons representative of Fuel Oil No. 4, Fuel Oil No. 6 and Residual Fuel Oil based on Environment Canada (2014).
# 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
 Table E-2. An analysis of experimental and modelled bioaccumulation data for petroleum hydrocarbons representative of Fuel Oil No. 4, Fuel Oil No. 6 and Residual Fuel Oil based on Environment Canada (2014).
# 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

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Appendix F: Ecotoxicological Information

Table F-1a. Aquatic toxicity of Fuel Oil No. 6

Fish
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
Invertebrates
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
Algae
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
Table F-1b. Aquatic toxicity of light and heavy Residual Fuel Oil (CAS RN 68476-33-5)
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
Table F-2. Acute systemic toxicity data for Fuel Oil No. 6 (CONCAWE 1998)
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
Table F-3. Estimated volume of water in contact with high persistence oil (m3 × 106) for loading/unloading and transport processes of oil via ship for various spill sizes (RMRI 2007)
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

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Appendix G: Summary of Health Effects Information for Fuel Oil No. 4, Fuel Oil No. 6, Residual Fuel Oil and Related HFOs

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
 
Initiation: A dose of 16.8 mg/kg-bw (50 μL of catalytically cracked clarified oil at 1% in toluene)[c],[f],[l]was applied to groups of male CD mice (30 per group) for 5 consecutive days. After a 2-week rest period, the promoter phorbol-12-myristate-13-acetate (PMA) was applied 2 times per week for 25 weeks. A significant increase in skin tumour incidence was observed (26/30 exposed mice developed tumours after 16 weeks).
Promotion: Details of study design not provided. No increase in histologically confirmed tumour incidence. However, a statistically significant increase in the number of mice with gross masses and shortened latency periods were observed, suggesting a possible weak promoting activity (API 1989).

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.
(1) Teratogenic effects per gestation day (2000 mg/kg): The greatest incidence of resorptions/decreased litter size occurred on GDs 11–12. Fetal body weights were reduced on all GDs. The greatest incidence of fetal external anomalies and visceral malformations occurred on GDs 12–14 and 12–13, respectively. Various fetal skeletal malformations occurred on all GDs.
(2) Teratogenic effects per dose (GD 12): There was a dose-related response for increased resorptions, decreased litter size, decreased fetal body weight and increased incidence of fetal skeletal malformations. A variety of fetal external anomalies were also observed at 2000 mg/kg (Feuston and Mackerer 1996).

Genotoxicity – in vivo 64741-62-4

Unscheduled DNA Synthesis
Groups of male Fischer 344 rats (3 animals per dose) were administered by oral gavage a single dose of 50, 200 or 1000 mg/kg-bw of test substance, 2 or 12 hours before sacrifice. A significant increase in UDS in primary hepatocyte cultures was observed at 200 mg/kg-bw (after 12 hours only) and 1000 mg/kg-bw (after 2 and 12 hours) (API 1985a).

Sister Chromatid Exchange
Groups of male and female B6C3F1 mice (5 animals per sex per dose) were administered 400, 2000 or 4000 mg/kg-bw test substance via intraperitoneal injection. A significant increase in sister chromatid exchange (SCE)/metaphase in bone marrow cells was observed at greater than or equal to 2000 mg/kg-bw (male; P less than 0.05) and at 4000 mg/kg-bw (female; P less than 0.01). The effect exhibited a positive dose-dependent trend at all doses (API 1985b).

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 in S. typhimurium TA1535, TA1537, TA98 and TA100 with and without S9 metabolic activation (NTP 1986).

Test substance was negative inS. typhimurium TA98 with and without S9 metabolic activation (Schultz et al. 1981).

Inhibition of Morphological Transformation
Test substance was negative in ST-FeSV-infected human foreskin fibroblasts without metabolic activation (Blakeslee et al. 1983).

Genotoxicity – in vivo 68553-00-4

Mutagenicity
S. typhimurium TA1535, TA1538, TA98 and TA100 were exposed with and without S9 metabolic activation (Aroclor 1254-induced rat liver). Mutagenicity was not observed (Vandermeulen et al. 1985).

Test substance was also negative in a forward mutation assay using Chlamydomonas reinhardtii (Vandermeulen and Lee 1986).

Sister Chromatid Exchange
Chinese hamster ovary cells were exposed with and without S9 metabolic activation (Aroclor 1254-induced rat liver). No increase in SCE was observed (Farrow et al. 1983).

Mouse Lymphoma Assay
L5178Y TK+/- cells were exposed to test substance with and without S9 metabolic activation (Aroclor 1254-induced rat liver). Mutant frequency did not increase (Farrow et al. 1983).

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
Primary rat hepatocyte cultures derived from F-344 male rat liver were exposed to ethanol dilutions of aromatic pyrolysis oilat concentrations of 0.5, 2, 10 or 60 μg/mL for 18–20 hours (without S9 metabolic activation). A concentration-response was observed for UDS at greater than or equal to 2 μg/mL (Brecher and Goode 1984).

Mutagenicity
Chinese hamster ovary cells were exposed to ethanol dilutions of aromatic pyrolysis oil at concentrations of 32, 64, 96, 128, 175 or 256 μg/mL without S9 metabolic activation (Aroclor-1254 induced rat liver) and 128, 175, 256, 375, 512 or 750 μg/mL with S9 metabolic activation. A repeat experiment was conducted at concentrations of 500, 600 or 750 μg/mL with S9 metabolic activation. Reduced cell count was observed at all concentrations (with and without S9) and significant toxicity was observed at all concentrations with S9. An increase in mutant frequency was definitive at 750 μg/mL with an observed linear concentration-related trend for mutagenicity at lower concentrations. In the repeat experiment, an increase in mutant frequency was observed at 500 μg/mL (and the higher concentrations were toxic). No mutagenic effects were observed without S9 metabolic activation (Papciak and Goode 1984).

Genotoxicity – in vivo 64741-62-4

Sister Chromatid Exchange
Chinese hamster ovary cells were exposed to the test substance at concentrations of 5–100 μg/mL without S9 metabolic activation and 100–5000 μg/mL with S9 metabolic activation. An increase in SCE was observed with activation. No increase in SCE observed without activation (API 1985e).

Cell Transformation
BALB/3T3 mouse embryo cells were exposed to the test substance at concentrations of 1, 3, 6 or 9 μg/mL without S9 metabolic activation (for 3 days) or 10, 30, 100 or 300 μg/mL with S9 metabolic activation (for 4 days). S9 was prepared from Aroclor-induced male rat liver. An increase in the frequency of transformation was observed at 100 μg/mL after 4 hours. Low survival rates were observed at 300 μg/mL. No increase in morphological transformation without activation (API 1986b).

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2024-05-16