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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 254-052-6 | CAS number: 38640-62-9
- 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
Link to relevant study record(s)
Description of key information
DIPN is absorbed and metabolized quite fast after administration and might accumulate in fat tissue during repeated exposure. In fat, elevated levels are attained. But the concentration reached is dependent on dose and not on duration of exposure. Thus extended exposure will presumably not result in continuing accumulation of DIPN. Based on dosage a maximal level (steady state) will be reached without further accumulation. After cessation of exposure, elimination of DIPN from fat will occur with a half-life of approx. 50 to 300 h (biphasic elimination characteristics).
Key value for chemical safety assessment
Additional information
Basic toxicokinetics
Information on DIPN
DIPN is absorbed from the gastrointestinal tract quite rapidly (Kawai/Iwahara 1974). It is distributed in the body and peak levels in blood and organs are reached within about 2 h (single dose administration). In adipose tissue, peak levels are attained considerably later (24 h p.a.). Tissue concentration in fat (ca. 90 µg/g) is higher than in other tissues (≤ ca. 30 µg/g). DIPN is cleared from organs quite rapidly and elimination is complete after 48 h. In fat, ca. 70% of the peak level is still found after 48 h (Hazegawa 1982_in vivo).
After repeated dose oral administration, final tissue levels are dependent on dose but not on exposure period (Anbe 1980). Organ concentrations of DIPN are in the same order as for single administration. But fat levels are doubled. Clearance of DIPN from organs is quite rapid and complete within 1 to 3 d thus comparable with single dose administration. In fat, elimination is much slower with still 4% DIPN present after 30 days (Hazegewa 1982_in vivo).
Elimination from organs indicates metabolic transformations. Metabolism was demonstrated by reaction of DIPN with liver homogenates showing decomposition rates of 40 to 50% within 2 h depending on the initial concentration (Hazegawa 1982_in vitro). Metabolites of DIPN (labeled substrate) in urine have been separated by TLC (Kawai/Iwahara 1974). But discrete metabolites of DIPN have not yet been isolated and characterized.
After single oral administration of 3H labeled DIPN, radioactivity is completely excreted within 96 h (30% in urine, 70% in feces). Native DIPN was not detected (Kawai/Iwahara 1974).
Information on supporting substance 2,6-DIPN
Comparable studies have been performed with 2,6-DIPN. This compound will be used as supporting substance.
For 2,6-DIPN similar results on absorption and distribution have been observed supporting the findings for DIPN (Kojima 1978, Kojima 1979). In addition, five metabolites were identified. In urine and bile, 40% of the total dose was excreted in form of these metabolites within 24 h after single oral administration of unlabeled native 2,6-DIPN. Two further metabolites were separated in TLC without elucidation of their structure. The metabolites identified are all transformed in the isopropyl side chain. The unidentified metabolites are considered to be phenolic compounds due to reaction with diazotized sulfanilic acid (Kojima 1982/1985).
Main facts
Overall, DIPN is absorbed and metabolized quite fast after administration and is not accumulated in organs during repeated exposure. However, in fat tissue, elevated levels are attained. But the concentration reached is dependent on dose and not on duration of exposure. Thus extended exposure will presumably not result in continuing accumulation of DIPN. Based on dosage a maximal level (steady state) will be reached without further accumulation. After cessation of exposure, elimination of DIPN from fat will occur with a half-life of approx. 50 to 300 h (biphasic elimination characteristics).
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.