Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 273-489-3 | CAS number: 68987-29-1
- 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
Administrative data
Description of key information
Subchronic (90-day) study oral (gavage), rat (Sprague-Dawley) m/f (OECD guideline 408, GLP): NOAELneurotoxicity: 1000 mg/kg bw/day (both sexes); read-across substance Phosphoric acid, C9-15 branched and linear alkyl esters, potassium salts
Key value for chemical safety assessment
Effect on neurotoxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 000 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- The available study is a high quality guideline study with original RL1. In accordance to the ECHA guidance document “Practical guide 6: How to report read-across and categories (March 2010)”, the reliability was changed from RL1 to RL2 to reflect the fact that this study was conducted on a read-across substance.
Effect on neurotoxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Effect on neurotoxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Reliable data on neurotoxicity of PAE are available from a 90-day gavage study in rats on the read-across substance Phosphoric acid, C9-15 branched and linear alkyl esters, potassium salts.
The read-across approach is appropriate due to similar composition of source and registered substance. From the available data is can be concluded that the repeated dose toxicity of substances with different alkyl moieties (C12, C14, C9-15 linear and branched) is comparable.
Phosphoric acid alkyl esters are hydrolysed unspecifically by phosphatases, e.g. acid phosphatase or alkaline phosphatase. Both enzymes are found in most organisms from bacteria to human. Alkaline phosphatases are present in all tissues, but are particularly concentrated in liver, kidney, bile duct, bone and placenta. In human and most other mammals three isoenzymes of Alkaline phosphatase exist: intestinal ALP, placental ALP, tissue non-specific ALP (present in bone, liver, kidney, skin).
Seven different forms of Acid phosphatase are known in humans and other mammals. These are also present in different tissues and organs (predominantly erythrocytes, liver, placenta, prostate, lung, pancreas).
Linear and branched primary aliphatic alcohols are oxidised to the corresponding carboxylic acid, with the corresponding aldehyde as a transient intermediate. The carboxylic acids are further degraded via acyl-CoA intermediates in by the mitochondrial beta-oxidation process. Branched aliphatic chains can be degraded via alpha- or omega-oxidation (see common text book on biochemistry).
“The long chain aliphatic carboxylic acids are efficiently eliminated and aliphatic alcohols are therefore not expected to have a tissue retention or bioaccumulation potential (Bevan, 2001).
Longer chained aliphatic alcohols within this category may enter common lipid biosynthesis pathways and will be indistinguishable from the lipids derived from other sources (including dietary glycerides) (Kabir, 1993; 1995 a,b).
A comparison of the linear and branched aliphatic alcohols shows a high degree of similarity in biotransformation. For both sub-categories the first step of the biotransformation consists of an oxidation of the alcohol to the corresponding carboxylic acids, followed by a stepwise elimination of C2 units in the mitochondrial β-oxidation process. The metabolic breakdown for both the linear and mono-branched alcohols is highly efficient and involves processes for both sub-groups of alcohols. The presence of a side chain does not terminate the β-oxidation process, however in some cases a single Carbon unit is removed before the C2 elimination can proceed.” (OECD SIDS, 2006)
The PAEs with branched fatty alcohols can be considered as a worst case scenario because the metabolism of the resulting branched fatty acids occurs less efficient compared to linear fatty acids.
In a subchronic toxicity study according to OECD guideline 408 Phosphoric acid, C9-15 branched and linear alkyl esters, potassium salts (34.35% a. i.) was administered to 5 Sprague-Dawley rats/sex/dose by oral gavage at dose levels of 0 (control), 8, 40, 200 and 1000 mg/kg bw/day). The animals were dosed for 91 days. Additional 5 males and 5 females were added to the control group and 1000 mg/kg group as a recovery group to examine the reversibility of the effects. Those animals were observed for another 14 days.
No adverse reaction was observed in hematology, blood biochemistry or organ weight measurement. Concerning neurological toxicology and behavior toxicology, no toxic effect was seen in detailed clinical observation, sensory response test, grip strength test, or histopathological examination of neurological organs and tissues. No change was noted in ophthalmological examination.
The changes observed during the dosing period or at the end of the dosing period such as salivation, abnormal respiratory sound, low body weight, low urine pH, thickening of the forestomach mucosa, dilatation of cecum, hyperplasia and erosion of squamous cells of the forestomach and hypertrophy of the cortical glomerular zone of the adrenal gland were not observed during the recovery period or at the end of the recovery period except for the change in the adrenal gland. The change in the adrenal gland also became milder and these changes were confirmed to be reversible.
The above results show that toxic effect after repeated oral administration of Phosphoric acid, C9-15 branched and linear alkyl esters, potassium salts appears mainly in the adrenal gland and forestomach.
The NOAEL for neurobehavioural effects is 1000 mg/kg bw/d in both sexes.
The BMDL10 for overall effects (adrenal gland, for details see repeated dose toxicity part of this study) is 240.30mg/kg bw/d (corresponding BMD =374.61 mg/kg bw/d).
There is no data gap in neurotoxicity. There is no reason to believe that results of the study would not be relevant for neurotoxicity in humans and, therefore, for risk assessment.
Justification for selection of effect on neurotoxicity via oral route endpoint:
OECD guideline study, no deviations, GLP; 90 d study
Justification for classification or non-classification
In conclusion, the results of the available data on neurotoxicity indicate that 1-Octadecanol, phosphate, potassium salt does not need to be classified according to Directive 67/548/EEC as well as CLP, EU GHS (Regulation 1272/2008/EC) and therefore labelling is not necessary.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.