Registration Dossier
Registration Dossier
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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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
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EC number: 203-047-7 | CAS number: 102-69-2
- 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
Description of key information
Additional information
JUSTIFICATION FOR DATA WAIVING
According to Regulation (EC) 1907/2006, Annex IX, Section 9.4.1 to
9.4.3, Column 2, studies on the toxicity to terrestrial organisms do not
need to be conducted if direct and indirect exposure of the soil
compartment is unlikely.
For tripropylamine only industrial and professional uses with adequate
risk mitigating measures are foreseen. Environmental exposure through
widespread uses by consumers is excluded. Widespread uses by
professionals will mostly take place indoors. In case of outdoor
scenarios, risk mitigating measures are implemented to reduce unintended
exposure to insignificant amounts. The substance is not supposed to be
directly applied to soil.
Tripropylamine is considered not readily biodegradable according OECD
criteria, however shown to be easily eliminated from water, after an
extended lag phase (see IUCLID Ch. 5.2.1). Therefore, an indirect
exposure to soil via sewage sludge transfer may be reduced since it can
be assumed that the substance will partly be biodegraded within the STP
process and as a consequence a transfer to the soil compartment is
minimized. Additionally, adsorption to sewage sludge is not expected
based on the low adsorption potential (see IUCLID Ch. 5.4.1); therefore,
further reducing the risk of indirect transfer of the substance via
sewage sludge.
In Annex XI, Section 3, it is laid down that testing in accordance with
Annex IX may be omitted, based on the exposure scenario(s) developed in
the Chemical Safety Report (“Substance-Tailored Exposure-Driven
Testing”). In accordance with Annex XI, Section 3, it can be
demonstrated in the risk assessment that the manufacture and the use of
the substance do not pose an unacceptable risk for all environmental
compartments as the risk characterization ratios (RCRs) of the chemical
safety assessment are well below 1 for all compartments (see Chemical
Safety Report Ch. 10).
Consequently, no tests on soil organisms are performed. The equilibrium
partitioning method has been used for assessing the hazard to soil
organisms in accordance with Annex IX, Section 9.4, Column 2 of
Regulation (EC) No 1907/2006.
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.