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EC number: 208-584-0 | CAS number: 534-03-2
- 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
Genetic toxicity in vitro
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Genetic toxicity in vivo
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
There are no data available on genetic toxicity of 2 -amino-1,3-propanediol (APD). However, there are reliable data for another member of the chemical category APD belongs to. Therefore, read-across was performed based on a category approach. Within this chemical category, the members are 2-amino -1,3-propanediol (APD), 2-amino-2-methyl-1,3-propanediol (AMPD) and AEPD, collectively called aminopropanediols. All the members contain a propane backbone carrying the same functional groups, one primary amine group and two hydroxyl groups, at the same position. The three category members differ only in the length of the alkyl side chain, which contains 0, 1 or 2 carbon atoms for APD, AMPD and AEPD, respectively. The modelling of potential metabolites via the OECD QSAR toolbox v.2.0 (2010) did not predict relevant metabolites of the category members. Based on the chemical structure of the parental compounds, no metabolism is expected. Therefore, it can be assumed that aminopropandiols will not show reactive properties under in-vitro and in-vivo test conditions.
All the category members are of low concern with regard to systemic toxicity. Available studies via the oral, dermal and intraperitoneal route indicate low acute and repeated dose toxicity. Inhalation is of no concern, because the low vapour pressure means that exposure is unlikely to occur.The results of the acute studies, as well as the repeated dose studies, demonstrate that the main cause of toxicity was the intrinsic alkalinity of the category members at the site of contact.The Cramer classification (related mainly to the oral route) also indicates a low toxicological concern for all the category members. No metabolism by cytochrome P450 enzymes in-vivo is expected; this is supported by predictions from QSAR modelling. With respect to molecular structures, no mutagenic potency is predicted using QSAR modelling and no structural alerts were detected. “H-acceptor-path3-H-acceptor” is alerted in a large number of molecules and thus of practically no prediction value. Due to the structural similarity between the members of the category and the similar toxicological properties, APD, AMPD and AEPD form a robust chemical category and read-across within this category is justified. In conclusion, it is considered appropriate to read-across from AEPD (CAS 115-70-8) to APD within the category approach.
The in vitro genetic toxicity of AEPD was investigated in a bacterial reverse mutation assay (Ames test) according to OECD 471 (Mochizuki, 2004). The preincubation method was conducted with S. typhimurium strains TA 1535, TA 1537, TA 98, TA 100 and E. coli WP2 uvrA at concentrations up to 5000 µg/plate. AEPD did not induce reversions in any of the S. typhimurium strains or in E. coli WP2 uvrA with or without metabolic activation. No cytotoxic effects were observed and all positive controls were valid.
In a study according to OECD 473, the potential of AEPD to induce chromosomal aberrations was tested in cultured Chinese hamster lung (CHL) cells (Sono, 2004). CHL cells were exposed to AEPD at concentrations up to 1200 µg/mL. No increase in chromosomal aberrations was observed in the experiments with short-term treatment (6 h) in the presence or absence of metabolic activation. No cytotoxic effects were observed and the positive controls were valid. Because of the negative results of the short-term treatment, an additional testing without metabolic activation was performed with continuous treatment (24 and 48 h). After continuous treatment, AEPD did not induce chromosomal aberrations in CHL cells.
AEPD was also tested for its potential to cause gene mutations in an in-vitro mammalian cell mutation assay according to OECD 476 (Indrani, 2011). Chinese hamster ovary (CHO) cells were treated with AEPD at concentrations of up to 1192 µg/mL for 4 h both with and without metabolic activation. After an expression time of 9 days in growth medium, cells were incubated for 10 days with 6-thioguanine as selection agent for forward mutation at the HPRT locus. Both with and without metabolic activation, no increases in mutant frequency were observed in the initial and in the conformatory gene mutation assay. At the highest tested concentration, AEPD caused cell growth inhibition, evaluated by relative cloning efficiency.
Taking into account all available data, AEPD
showed no evidence of a clastogenic and mutagenic potential with and
without metabolic activation in in-vitro test systems. Therefore,
it can be assumed that APD possesses no genotoxic potential. Based
on read-across within the chemical category, APD is considered to be not
genotoxic.
Justification for classification or non-classification
Based on read-across within the chemical category, the available data on genetic toxicity do not meet the criteria for classification according to Regulation (EC) 1272/2008 or Directive 67/548/EEC, and are therefore conclusive but not sufficient for classification.
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