Registration Dossier
Registration Dossier
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: 700-960-7 | CAS number: 68512-30-1
- 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

Endpoint summary
Administrative data
Description of key information
Constituents of OAPP show signs of environmental persistence, based on QSAR and experimental results. For further clarification, OAPP is subject of a substance evaluation process (CoRAP) (ECHA draft decision of 03 May 2019). Proposal: an enhanced ready-biodegradability test be carried out on a relevant dimer constituent, 1,1,3-trimethyl-3-phenylindan [CAS no. 3910-35-8] (Status 05 May 2019).
Additional information
Stability
Phototransformation in air
No data available (not required for REACH)
Hydrolysis
The substance Oligomerisation and alkylation reaction products of 2-phenylpropene and phenol (OAPP, phenol, methylstyrenated) contains constituents of the category phenols and phenyl substituted aliphatic compounds. These do not possess functional groups that are regarded as being susceptible to hydrolysis under environmental conditions. The test substance is considered to be not hydrolysable.
Phototransformation in water
No data available (not required for REACH)
Phototransformation in soil
No data available (not required for REACH)
Biodegradation
Biodegradation in water: screening tests
The substance oligomerisation and alkylation reaction products of 2-phenylpropene and phenol (OAPP, phenol, methylstyrenated) was not readily biodegradable under standard test conditions according to OECD TG 310 [CO2 in Sealed Vessels (Headspace Test)]. This finding is confirmed by a negative result on biodegradability of p-cumylphenol [CAS No. 599 -64 -4], a monostyrenated key component of the test substance, in a study according to OECD TG 301C.
Biodegradation in water and sediment: simulation tests
No data available
Biodegradation in soil
No data available.
Mode of degradation in actual use
No data available (not required for REACH)
Bioaccumulation
Bioaccumulation: aquatic / sediment: dietary exposure - OAPP = UVCB target compound
The bioaccumulation properties of the target substance OAPP have been investigated in a fish test (OECD 305, feeding variant). The study revealed that only the Dimers and Trimers of test material OAPP show a potential to be biomagnified. The lipid-corrected BMF values were 0.073 and 0.1374 for the dimers and trimers, respectively, both active ingredients of the test material. The growth-corrected half-lives were found to be 5.3 and 25.8 days, respectively. The corresponding BCF values, calculated on the basis of several approaches published in the literature are in the order of ≤ and ≥ 2000 for the dimers, and ≥ 5000 for the group of the trimers (further details in the ‘Bioaccumulation assessment’ document in the ‘Attached background material’ section). Uncertainty in these values are based on uncertainties in the conversion method employed.
Bioaccumulation: aquatic / sediment: aqueous exposure - constituents
No data is available on the target substance OAPP itself. p-Cumylphenol [CAS No. 599 -64 -4], a monostyrenated key component of the target substance, showed little bioaccumulating potential in fish, when, tested in a valid standard bioaccumulation study according to OECD 305 (via water-phase).
The BCF values ranged from 65 to 190 after 8 weeks of exposure.
For one non-phenolic key constituent, the dimer 1,1'-(1,1-dimethyl-3-methylene-1,3-propanediyl)bisbenzene (4-methyl-2,4-diphenylpent-1-ene) [CAS no. 6362-80-7], a reliable Japanese bioaccumulation study in fish (MITI-I protocol, according to OECD 305) is available (NITE 2002). Carps (Cyprinus carpio) were exposed for 60 days to two concentrations - 1 and 10 μg/L - with depuration for 16 days included. After normalisation to a lipid content of 5 %, the mean BCF values of two replicates were as follows (note: re-calculated to 5% lipid by the applicant):
High exposure: 2015 (day 42) / 3210 (day 60)
Low Exposure: 3890 (day 42) / 1750 (day 60).
The mean BCFs at steady state (day 28 to 60) are approx. 2320 L/kg (10 µg/L) and 2767 L/kg (1 µg/L). Based on these two values, bioaccumulation is assessed to be moderate rather than very high. The 60d value of <2000 at the low exposure level may indicate that the bioconcentration potential is low, but no firm conclusions can be drawn from the limited database.
Depuration following bioaccumulation
Elimination half-lives (as DT50) were given as 4.5 d (at the high exposure of 10 µg/L) and as 15.7 d for the low exposure (1 µg/L) (NITE 2002). A critical examination of the data evaluation in the report suggests that at least the comparatively long DT50 of 15.7 d is erroneous. A simple comparison of the initial tissue concentration (100%) with the residual one after 9 days suggest that the elimination half-lives are as follows (assuming first-order elimination kinetics):
High exposure (10 µg/L): decrease ~95%/9d = ~4 T/2 --> DT50 = ~2.3d
Low exposure (1 µg/L): decrease ~83%/9d = ~2.7 T/2 --> DT50 = ~3.3d.
These findings are consistent with low to moderate bioaccumulation potential for the non-phenolic dimers of oligomerisation and alkylation reaction products of 2-phenylpropene and phenol.
Bioaccumulation: terrestrial
No data available (not required for REACH)
Transport and distribution
Adsorption/Desorption
The substance oligomerisation and alkylation reaction products of 2-phenylpropene and phenol (previous name phenol, methylstyrenated) contains components with high log Pows ranging from 3.6 to ≤ 6.3. Corresponding adsorption constants (organic matter - water), log Koc, calculated from the log Pow are expected to range from 3.24 - 5.90 (based on Karickhoff 1981: log Koc = 0.989 x log Pow - 0.346). Moreover, water solubility is low (1 - 7 mg C/L at a loading of 100 mg/L). These properties indicate high adsorption and low mobility in soil.
Based on a log Pow of 6.3 (see Chapter 1.3), a log Koc of 5.88 (Koc = 760,000) is calculated for the substance using the relation of Karickhoff.
The Henry's law constant was estimated to be 3.278 Pa*m³/mol using the vapour pressure (0.044 Pa), the water solubility (4 mg/L), and the average molecular weight (298 g/mol) of the substance (see Chapter 1.1 and 1.3).
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.

EU Privacy Disclaimer
Ce site web utilise des cookies afin de vous garantir la meilleure expérience possible sur nos sites web.