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EC number: 249-535-3 | CAS number: 29253-36-9
- 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
Additional information
Stability
Phototransformation in air
For 2-isopropylnaphthalene (2-IPN) [CAS No. 2027 -17 -0], a constituent of the substance isopropylnaphthalene (MIPN) [CAS No. 29253-36-9] at approx. 65 %, the half-time of decomposition (DT50%) was 20 to 30 h, when the test material had been coated onto the glass wall of the test tube or adsorbed onto filter paper under artificial UV-test conditions (simulated sunlight).
Hydrolysis
Due to its chemical structure, isopropylnaphthalene (MIPN) cannot be hydrolysed. The structure of the molecule does not contain any hydrolysable groups.
Phototransformation in water
Using a high-pressure mercury lamp as irradiation source (simulated sunlight), the photolytic half-life of 2-isopropylnaphthalene (2-IPN), was approx. 22 h in distilled water (elimination constant 0.031/h), while it was only approx. 1 h in the presence of salt (0.5 M NaCl).
Phototransformation in soil
No data available (not required for REACH)
Biodegradation
Biodegradation in water: screening tests
In a valid follow-up study applying the OECD method 310 (Ready Biodegradability - CO2 in Sealed Vessels, Headspace Test), biodegradation of 60 % was reached after 23 d within a 12-days window, hence just failing the 10-days window (Fiebig/NOACK 2013). GC-analysis demonstrated >99% elimination of the original substance after 16 days. In a MITI II test (OECD 302 B, 28 d) using a concentration of 30 mg/L of MIPN, only poor biodegradation was observed with a low BOD of about 12 %. However, GC-analysis suggested significant primary degradation under test conditions (removal of the pristine test substance of about 93 %). This study has been disregarded, because a negative selective stress usually imposed on the inoculum in these Japanese investigations favour the loss of indigenous potent microorganisms carrying special properties of decomposition.
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
In a valid guideline test (OECD 305) [NITE Japan 2011, report date 1982], using flow-through conditions, mean BCF values at steady-state (time 4 to 8 wks) reached 870 and 640 at 50 and 5 µg/L, respectively. Tentative DT50 depuration times can be estimated to be about 1.5 to 2 days. There was no evidence of a high bioaccumulating potential under the standard test conditions applied.
Bioaccumulation: terrestrial
No data available (not required for REACH)
Transport and distribution
Adsorption/Desorption
Koc for isopropylnaphthalene was estimated to be 7455 using the calculation tool US EPA EPI Suite). Accumulation of MIPN in soil and/or sediment is to be expected.
Henry’s Law constant
Using measured values for vapour pressure and water solubility, Henry's Law constant was determined to be 147 Pa*m³/mol indicating quite rapid volatilisation of MIPN from water into air.
Distribution Modelling
Results of distribution modelling with a Fugacity level III model give evidence that MIPN is distributed mostly into soil (ca. 86%) and to a much lesser degree into water (ca. 9%) and sediment (ca. 4%). Percentage in air is minimal (ca. 0.4%).
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