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EC number: 225-218-5 | CAS number: 4724-48-5
- 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
Additional information
OPA has been evaluated for genotoxicity using a range of in vitro and in vivo assays covering endpoints of gene mutation, chromosomal damage and DNA repair.
In vitro,OPA consistently gave negative results in the Ames test in S typhimurium strains TA 1535, TA 1538, TA98, TA 100 and E Coli strains WP2P, WP2Puvr A and WP2 uvr A, both in the presence and absence of S9. In two out of five studies, Salmonella strain TA 1537, small increases in revertant colonies were seen on some occasions only in the presence of S9. In the mammalian cell mutation assay in L5178Y cells, small increases in mutant frequency were seen with one sample of OPA, but only in the absence of S9. A second sample showed no such increases. In an in vitro cytogenetic assay in human lymphocytes, OPA gave a negative response in both the presence and absence of S9. The weak nature of the increases seen in the Ames and L5178Y assays, the lack of reproducibility with samples, lack of consistency regarding requirements for S9 and lack of rationalisation against the chemical structures of the components of OPA lead to the conclusion that they do not indicate a significant genotoxic hazard for OPA.
In vivo,OPA has been shown to be negative in the mouse bone marrow micronucleus assay for clastogenicity and in the rat liver UDS assay for general DNA damage/DNA repair. These two in vivo assays, using dose levels up to and including the maximum tolerated dose levels, confirm that OPA is not genotoxic in the entire animal.
It is concluded that OPA has no significant genotoxic potential and does not pose a genotoxic hazard for animals or man.
Justification for selection of genetic toxicity endpoint
No study was selected, since OPA has been evaluated for genotoxicity using a range of in vitro and in vivo assays.
Short description of key information:
Octylphosphonic acid (OPA) has been evaluated for genotoxicity using a range of in vitro and in vivo assays, all evaluated as Reliability 1 and 2.
in vitro:
- Bacterial mutagenicity (Ames test): negative in 3 studies (Thompson, 1994, 1997; muller, 1988) but weakly positive only in S.typhimurium TA 1537 with activation in 2 studies (Callendar, 1997a, 1997b)
- Mutagenicity in mammalian cells: weakly positive without activation only in one L5178Y TK (+/-) Assay (Clay, 1997a) but negative in a repeat of the same assay using a different batch of test substance (Clay, 1997b).
- Clastogenicity/Aneugenicity in mammalian cells: negative in a chromosome aberration test in human lymphocytes (Fox, 1997a).
in vivo:.
- Clastogenicity/Aneugenicity: negative in a mouse bone marrow micronucleus test (Fox, 1997b).
- DNA damage/repair: negative in the UDS assay in rat liver (Fox, 1997c).
Endpoint Conclusion: No adverse effect observed (negative)
Justification for classification or non-classification
Based on absence of mutagenicity in the UDS study in vivo and absence of clastogenicity in a mouse micronucleus study in vivo, it is concluded that the OPA is not genotoxic. Therefore no classification is required according to the EU criteria.
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