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EC number: 266-417-7 | CAS number: 66587-56-2
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Description of key information
No data
Effect on fertility: via oral route
- Dose descriptor:
- NOAEL
- 2 000 mg/kg bw/day
Additional information
The multi-constituent alcohol identified as “Alcohols C7-9 linear and branched” includes the following mixture:
Alcohols C6-12 type C: >80% linear; > 95% C7/8/9 [range C6-C10]; even & odd (CAS 68603-15-6).
No studies on toxicity to reproduction/fertility performed to international guidelines were available on Alcohols C7-9 linear and branched by any route and the relevant data available from a repeated dose toxicity study are very limited.
In a research publication, the test material (Linevol 79) was dissolved in polyethylene glycol 300 and administered to male rats by oral gavage at 128 mg/kg bw/day for 14 days. There were no adverse effects on testis weight relative to body weight; absolute testis weight data were not presented. An NOAEL of 128 mg/kg bw/day was identified from this very limited study (Rhodes et al. 1984).
The Category hypothesis is that the long chain linear aliphatic alcohol family has at its centre an homologous series of increasing carbon chain length, which is associated with a consistency and predictability in the property data across the group, for the physicochemical, environmental and toxicological property data sets. In view of the structural and chemical similarities, it is considered that results from reproductive toxicity studies on single- or multiple-constituent alcohols with appropriate chain lengths could be read across to Alcohols C7-9 linear and branched.
In a combined repeat dose and reproductive/developmental toxicity screening test, performed in rats to draft OECD guideline 422 and to GLP, an oral NOAEL of 2000 mg/kg bw/day (the highest dose tested) was determined for Dodecanol for both the parental and F1 generations (Hansen 1992a).
A one-generation study was carried out with Docosanol in rats, following a protocol equivalent to OECD guideline 415 and to GLP. The NOAEL for the parental and the F1 generations was 1000 mg/kg bw/day, the highest dose tested (Iglesias 2000b).
A read-across feeding study reported a lack of effects on the reproductive organs of rats receiving Hexanol (NOAEL 1127 mg/kg bw/day) and no adverse effects were noted at any of the dose levels administered during the study (Scientific Associates Inc. 1966).
No studies on toxicity to reproduction were available on any of the long chain linear aliphatic alcohol family by the dermal or inhalation routes.
No two-generation reproductive toxicity studies were available for the long chain linear aliphatic alcohol family.
Chronic and sub-chronic toxicity studies have shown that long chain alcohols (LCA) are of low toxicity. Furthermore, combined repeated-dose studies with developmental endpoints, as well as reproductive and developmental studies showed no effects at the highest dose tested. Rather than having separate values for the three endpoints, one endpoint “systemic effects” has been used instead. Since the NOAELs do not vary greatly across the category, one key study has been chosen as being representative of the whole category.
C6, Hexanol has been chosen as the category representative because shorter chain molecules are usually regarded as more toxic when compared to structural analogues with longer carbon chain lengths.
Short description of key information:
No reproductive toxicity studies were available on Alcohols C7-9 linear and branched or on any alcohols with carbon chain lengths within that range. A reproductive screening test with Dodecanol was without effect on parental or F1 rats at 2000 mg/kg bw/day (Hansen 1992a) and in a one-generation study with Docosanol the NOAEL was 1000 mg/kg bw/day (Iglesias 2002b). A read-across feeding study reported a lack of effects on the reproductive organs of rats receiving Hexanol (NOAEL 1127 mg/kg bw/day) and no adverse effects were noted at any of the dose levels administered during the study (Scientific Associates Inc. 1966).
Effects on developmental toxicity
Description of key information
No developmental toxicity studies were available on Alcohols C7-9 linear and branched by any route. A reproductive screening test with Dodecanol was without effect on parental or F1 rats at 2000 mg/kg bw/day (Hansen 1992a). In a guideline study with Alcohols C7-11 branched and linear, the NOAEL for both maternal and developmental toxicity was 1440 mg/kg bw/day. Octanol gave an NOAEL for developmental toxicity of 1300 mg/kg bw/day, but maternal toxicity was seen at 130 mg/kg bw/day (Hellwig & Jackh 1997).
Effect on developmental toxicity: via oral route
- Dose descriptor:
- NOAEL
- 2 000 mg/kg bw/day
Additional information
The multi-constituent alcohol identified as “Alcohols C7-9 linear and branched” includes the following mixture:
Alcohols C6-12 type C: >80% linear; > 95% C7/8/9 [range C6-C10]; even & odd (CAS 68603-15-6).
No developmental toxicity/teratogenicity studies were available on Alcohols C7-9 linear and branched by any route.
The Category hypothesis is that the long chain linear aliphatic alcohol family has at its centre an homologous series of increasing carbon chain length, which is associated with a consistency and predictability in the property data across the group, for the physicochemical, environmental and toxicological property data sets. In view of the structural and chemical similarities, it is considered that the results from a number of reliable developmental toxicity/teratogenicity studies on single- or multiple-constituent alcohols with appropriate chain lengths can be read across to Alcohols C7-9 linear and branched.
A prenatal developmental toxicity study, performed to OECD guideline 414 and to GLP, was performed in rats dosed orally by gavage on days 6 to 15 of gestation with one of three long chain linear aliphatic alcohols. Clinical signs indicative of maternal toxicity were seen with Octanol at 130 mg/kg bw/day, the lowest dose tested, and an NOAEL of 1300 mg/kg bw/day, the highest dose tested, was seen for developmental toxicity. No maternal or developmental toxicity was seen with Alcohols C7-11 branched and linear at up to 1440 mg/kg bw/day and this top dose was therefore the NOAEL (Hellwig & Jackh 1997).
In a combined repeat dose and reproductive / developmental toxicity screening test, performed to draft OECD guideline 422 and to GLP, an oral NOAEL of 2000 mg/kg bw/day (the highest dose tested) was determined for Dodecanol for both maternal and developmental toxicity (Hansen 1992a).
No reliable guideline studies on developmental toxicity/teratogenicity were available on any of the long chain linear aliphatic alcohol family by the dermal routes.
Chronic and sub-chronic toxicity studies have shown that long chain alcohols (LCA) are of low toxicity. Furthermore, combined repeated-dose studies with developmental endpoints, as well as reproductive and developmental studies showed no effects at the highest dose tested.Rather than having separate values for the three endpoints, one endpoint “systemic effects” has been used instead. Since the NOAELs do not vary greatly across the category, one key study has been chosen as being representative of the whole category.
C6, Hexanol has been chosen as the category representative because shorter chain molecules are usually regarded as more toxic when compared to structural analogues with longer carbon chain lengths.
Toxicity to reproduction: other studies
Additional information
No data
Justification for classification or non-classification
Based on the available data, Alcohols C7-9 linear and branched would not be classified as toxic to reproduction under Regulation (EC) No. 1272/2008 (CLP) or Directive 67/548/EEC (DSD). Tests on similar substances included in this category are also supportive of these results, which do not warrant classification for toxicity to reproduction under DSD or GHS criteria.
Additional information
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