Name: Octane
CAS Number: 111-65-9
UN Number: 1262
Formulae: C8H18
Name: Octane
CAS Number: 111-65-9
UN Number: 1262
Formulae: C8H18
Physicochemical properties/Characteristics
-
FE
Physical behaviour (GESAMP, 2016)
1, 2 -
114.232
Molecular Weight
2
(g/mol) -
0.70
Density
2
(kg/L) -
1.88
Vapour pressure
2
(KPa; 25ºC) -
0.66
Water solubility
2
(mg/L; 25ºC) -
0.52
Dynamic viscosity
2, 3
(mPa.s; 25ºC) -
-56.8
Melting point (ºC)
2 -
125.7
Boiling point (ºC)
2 -
27.8
Volatilization half-life (days)
4
- G: gas; D: dissolver; E: evaporator; F: floater; S: sinker; GD: gas/dissolver; DE: dissolver/evaporator; FD: floater/dissolver; FE: floater/evaporator; FED: floater/evaporator/dissolver; Fp: persistent floater; SD: sinker/dissolver
- Values collected from the literature and public databases e.g. PubChem
- “-“ corresponds to values not found
- Values estimated with models of the EPI suiteTM
Fugacity/Persistence
-
6.82
Air
4, 5 -
92.00
Water
4, 5 -
0.00
Soil
4, 5 -
1.21
Sediment
4, 5 -
6.7
Persistence (days)
4
- Values estimated with models of the EPI suiteTM
- In the present study, only emissions in water were considered
Physicochemical degradation/Biodegradation
-
15.5
Atmosferic Oxidation (hours)
4 -
R
Biodegradation rate (GESAMP, 2016)
6, 7 -
0.86
Aerobic biodegradation probability
4 -
4.22 days
Primary aerobic biodegradation half-life
4, 8 -
3.54 days-weeks
Ultimate aerobic biodegradation half-life
4, 8 -
6.4
Hydrocarbon Biodegradation half-life (days)
3, 4 -
0.20
Anaerobic Biodegradation probability
4
- “-“ corresponds to values not found
- Values estimated with models of the EPI suiteTM
- Results obtained from the literature
- GESAMP criteria consider substances to be “readily biodegradable” (R) if, in 28-day biodegradation studies, the following levels of degradation are achieved: in tests based upon dissolved organic carbon (DOC) die-away: ≥ 70%; or in tests based upon oxygen depletion or carbon dioxide generation: ≥ 60% of the theoretical maxima; or where only chemical oxygen demand (COD) and biochemical oxygen demand (BOD5) data are available, the ratio of BOD5/COD ≥ 0.5; or where other convincing scientific evidence is available to demonstrate that the substance can be degraded (biotically and/or abiotically) in the aquatic environment to a level of > 70% within a 28-day period. Otherwise they are “not readily biodegradable” (NR) (GESAMP, 2014).
- See Table 1 in the supplementary material for more information on the rating reported by Boethling et al. (1994)
Bioaccumulation/Biotransformation
-
2.92
Biotransformation half-life (days)
2 -
5.18
Partition coefficient (log Kow)
2 -
1086.0
Bioconcentration factor (BFC)
4 -
5
Bioaccumulation rate (GESAMP, 2016)
9 -
3.57
Adsorption coefficient (log koc)
2
- Values collected from the literature and public databases e.g. PubChem
- Values estimated with models of the EPI suiteTM
- See Table 2 in the supplementary material for more information on Bioaccumulation rate classification (GESAMP, 2014)
Aquatic Toxicity
-
4
Acute toxicity (GESAMP, 2016)
10 -
-
Chronic toxicity (GESAMP, 2016)
3, 10
- “-“ corresponds to values not found
- See Table 3 in the supplementary material for more information on Aquatic Toxicity classification (GESAMP, 2014)
Acute Mammals/Human health effects
-
0
Oral Toxicity (GESAMP, 2016)
11 -
0
Dermal toxicity (GESAMP, 2016)
11 -
0
Inhalation toxicity (GESAMP, 2016)
11 -
0
Skin irritation & corrosion (GESAMP, 2016)
11 -
0
Eye irritation & corrosion (GESAMP, 2016)
11 -
0
Toxicity
12 -
0
Severity
12
- See Table 4 in the supplementary material for more information on Human health (Toxic effects to mammals) classification (GESAMP, 2014)
- For more information on Toxicity and Severity scores consult Harold et al. (2014)
Chronic Human/Mammals health effects
-
-
Carcinogenicity (IARC)
3, 13 -
No
Mutagenicity (GESAMP, 2016)
11 -
No
Reprotoxicity (GESAMP, 2016)
11 -
No
Sensitizing to skin (GESAMP, 2016)
11 -
Yes
Aspiration hazard (GESAMP, 2016)
11 -
No
Target Organ Toxicity (GESAMP, 2016)
11 -
No
Sensitizing to respiratory system (GESAMP, 2016)
11 -
No
Neurotoxicity (GESAMP, 2016)
11 -
No
Immunotoxicity (GESAMP, 2016)
11
- “-“ corresponds to values not found
- See Table 4 in the supplementary material for more information on Human health (Toxic effects to mammals) classification (GESAMP, 2014)
- See Table 5 in the supplementary material for more information on IARC classification
Toxicity tests results
PNECseawater:
0.005 µg/L
PNECwater, intermittent:
0.14 µg/L
Algae
-
EC50
Parameter
1 -
0.250
Concentration
(mg/L) -
Green algae
Species
-
-
Endpoint
-
Freshwater; 96h-exposure
Observations
1
-
MATC
Parameter
1 -
0.126
Concentration
(mg/L) -
Green algae
Species
-
-
Endpoint
-
Freshwater
Observations
2
- Values predicted with ECOSAR V1.11 (EPA) (accessed February 7, 2017)
Invertebrates
-
EC50
Parameter
1 -
0.12
Concentration
(mg/L) -
Common bay mussel - Mytilus edulis
Species
-
Feeding behaviour
Endpoint
-
Saltwater; Static; 15 °C; < 1.67h-exposure
Observations
3
-
EC50
Parameter
2 -
0.38
Concentration
(mg/L) -
Water flea - Daphnia magna
Species
-
Intoxication; immobilization
Endpoint
-
Freshwater; Static; 23 °C; 48h-exposure; 4-6d age
Observations
4
-
LC50
Parameter
3 -
0.100
Concentration
(mg/L) -
Daphnids
Species
-
Mortality
Endpoint
-
Freshwater
Observations
5
-
LC50
Parameter
4 -
0.4
Concentration
(mg/L) -
Brine shrimp - Artemia salina
Species
-
Mortality
Endpoint
-
Saltwater; Static; 20 °C; 24h-exposure; Nauplii
Observations
6
-
LC50
Parameter
3 -
0.014
Concentration
(mg/L) -
Mysid
Species
-
Mortality
Endpoint
-
Saltwater; 96h-exposure
Observations
7
Lowest
-
MATC
Parameter
3 -
0.022
Concentration
(mg/L) -
Daphnids
Species
-
-
Endpoint
-
Freshwater
Observations
8
-
MATC
Parameter
3 -
0.000487
Concentration
(mg/L) -
Mysid
Species
-
-
Endpoint
-
Saltwater
Observations
9
Lowest
- Donkin P et al; Aquat Toxicol 14 (3): 277-294 (1989) as cited in the ECOTOX database. Available at: http://cfpub.epa.gov/ecotox/quick_query.htm (accessed November 10, 2015)
- Bobra AM et al; Chemosphere 12 (9-10): 1121-1129 (1983) as cited in the ECOTOX database. Available at: http://cfpub.epa.gov/ecotox/quick_query.htm (accessed November 10, 2015)
- Values predicted with ECOSAR V1.11 (EPA) (accessed February 7, 2017)
- Abernethy S et al; Aquat Toxicol 8 (3): 163-174 (1986) as cited in the ECOTOX database. Available at: http://cfpub.epa.gov/ecotox/quick_query.htm (accessed November 10, 2015)
Fish
-
LC50
Parameter
1 -
0.131
Concentration
(mg/L) -
Fish
Species
-
Mortality
Endpoint
-
Freshwater; 96h-exposure
Observations
10
-
LC50
Parameter
1 -
0.168
Concentration
(mg/L) -
Fish
Species
-
Mortality
Endpoint
-
Saltwater; 96h-exposure
Observations
11
-
MATC
Parameter
1 -
0.018
Concentration
(mg/L) -
Fish
Species
-
-
Endpoint
-
Freshwater
Observations
12
-
MATC
Parameter
1 -
0.127
Concentration
(mg/L) -
Fish
Species
-
-
Endpoint
-
Saltwater
Observations
13
- Values predicted with ECOSAR V1.11 (EPA) (accessed February 7, 2017)
References
Boethling RS, Howard PH, Meylan W, Stiteler W, Beauman J, Tirado N. 1994. Group contribution method for predicting probability and rate of aerobic biodegradation. Environ. Sci. Technol. 28: 459-465.
Bonn Agreement, 1994. European Classification System, Bonn Agreement: Counter-Pollution Manual. Bonn Agreement, London (Chapter 25).
GESAMP (IMO/FAO/UNESCO-IOC/WMO/WHO/IAEA/UN/UNEP Joint Group of Experts on the Scientific Aspects of Marine Environmental Protection), 2014. Revised GESAMP Hazard Evaluation Procedure for Chemical Substances Carried by Ships, 2nd edition. Rep. Stud. GESAMP No. 64, 126 pp.
GESAMP Composite List, 2016. ANNEX 5 – UPDATED GESAMP COMPOSITE LIST. Available at: https://edocs.imo.org/Final Documents/English/PPR 1-CIRC.3 (E).docx (Accessed: December 12, 2016).
Harold PD, Souza AS, Louchart P, Russell D, Brunt H, 2014. Development of a risk based prioritisation methodology to inform public health emergency planning and preparedness in case of accidental spill at sea of hazardous and noxious substances (HNS). Environ. Int. 72: 157-163.