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EC number: 221-336-6 | CAS number: 3069-29-2
- 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
No long-term terrestrial toxicity data are available with N-[3-(dimethoxymethylsilyl)propyl]ethylenediamine (CAS 3069-29-2).
The substance hydrolyses rapidly to form N-[3-(dihydroxymethylsilyl)propyl]ethylenediamine and methanol. No biodegradation is expected for the silanol hydrolysis product, N-[3-(dihydroxymethylsilyl)propyl]ethylenediamine.
In the context of the Integrated Testing Strategy for the terrestrial compartment (ECHA guidance Chapter R.7c, terrestrial hazard classification scheme, Table R.7.11-2) (ECHA 2017) the aquatic toxicity tests do not indicate that the substance is very toxic (EC/LC50 >1 mg/L for algae, Daphnia and fish). However, despite rapid degradation of the parent substance, the silanol hydrolysis product may persist in the environment. The substance is therefore assigned to Hazard Category 3.
In this situation, a screening approach is applied: a confirmatory long-term terrestrial test is required in addition to the equilibrium partitioning approach with an extra factor of ten.
The PEC × 10 / PNECscreen based on the equilibrium partitioning method indicates the substance will have a risk characterisation ratio (RCR) >1. The highest terrestrial RCR based on PEC x 10 / PNEC is 4.69 related to deposition from air.
ECHA guidance Chapter R.7c, Table R.7.11-2 states the following: If PEC/PNECscreen >1 or indication of risk from confirmatory long-term soil toxicity test: Conduct long-term toxicity tests according to the standard information requirements Annex X (invertebrates and plants), choose lowest value for derivation of PNECsoil.
In accordance with the ECHA guidance, because the PEC/PNECscreen is >1 and the hydrolysis product is considered persistent in soil (DT50 >180 days), long-term terrestrial invertebrate and plant tests are proposed.
Although a short-term toxicity test has been carried out with structural analogue N-(3-(trimethoxysilyl)propyl)ethylenediamine (CAS 1760-24-3), with Eisenia foetida where no effects were observed at the highest tested concentrations (>1000 mg/l) (RCC, 2004), the REACH requirements are that long-term tests are performed.
In addition, toxicity was observed in the aquatic microorganism test, read across from a structural analogue (16 hour EC50 67 mg/L; EC10 25 mg/L (Pseudomonas putida, growth rate) (Diefenbach, 1994)). ECHA guidance Chapter R.7c states “Where inhibition of sewage sludge microbial activity has been observed in Annex VIII testing, a test on soil microbial activity will additionally be necessary for a valid PNEC to be derived.” A soil microorganisms nitrogen inhibition test (OECD 216) is therefore also proposed.
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.
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