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EC number: 815-305-1 | CAS number: 138938-64-4
- 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
The substance, 1-(tert-butyldimethylsilyl)piperazine is not stable in water, which affects the approach to the determination of physicochemical properties.
1-(Tert-butyldimethylsilyl)piperazine is a liquid at ambient temperature and pressure. It has a predicted density of 0.81 g/cm3 at 20°C and a predicted vapour pressure of 3.2 Pa at 25°C.
1-(Tert-butyldimethylsilyl)piperazine is not explosive and not oxidising on the basis of chemical structure.
In contact with water, the substance hydrolyses very rapidly at 25°C to form tert-butyldimethylsilanol and piperazine according to the following equation:
C10H24N2Si + H2O → C6H16OSi + C4H10N2
Therefore, requirements for testing of water-based physicochemical properties for the substance are waived on the basis of instability in water. The properties of the silanol hydrolysis product, tert-butyldimethylsilanol and piperazine are assessed instead.
Piperazine is freely soluble with water (O'Neil M J (ed) (2001)), has a low log Kow of -1.5 (Hansch et al 1995) and vapour pressure value of 21 Pa at 20°C (Kirk-Othmer 1978). Piperazine is positively charged at neutral pH and it is expected to bind theoretically to negatively charged soil particles and humus.
The silanol hydrolysis product; tert-butyldimethylsilanol, may undergo condensation reactions in solution to give siloxane dimers and a dynamic equilibrium is established. The overall rate and extent of condensation is dependent on nominal loading, temperature, and pH of the system, as well as what else is present in the solution. It may also change over time.
The condensation reactions of monosilanols may be modelled as an equilibrium between monomer and dimer. The reaction is reversible unless the dimer concentration exceeds its solubility; in this case, the dimer forms a separate phase, driving the equilibrium towards the dimer. For tert-butyldimethylsilanol, a solution at 100 mg/l (the highest concentration often used in ecotoxicity tests) is predicted to contain >99.9% monomer. At loadings above about 80 mg/l the concentration of the dimer is predicted to exceed its solubility, resulting in the formation of a separate phase. In addition, the dimer is expected to have a high volatility from water and this may cause losses from water under some conditions. Further information is given in a supporting report (PFA 2016am) attached in Section 13.
The water solubility of the silanol hydrolysis product (tert-butyldimethylsilanol) has been calculated using a validated QSAR estimation method to be 970 mg/l. However, the saturation concentration in reality may be limited by the formation of less soluble dimer rather than the solubility of the monomer itself. It has a predicted log Kow of 2.5 at 20°C and predicted vapour pressure of 64 Pa at 25°C.
References:
Hansch, C., Leo, A., D. Hoekman. Exploring QSAR - Hydrophobic, Electronic, and Steric Constants. Washington, DC: American Chemical Society., 1995., p. 10
Kirk-Othmer (1978). Kirk-Othmer Encyclopedia of Chemical Technology. 3rd ed., Volumes 1-26. New York, NY: John Wiley and Sons, 1978-1984., p. V2: 296 (1978)
O'Neil M J (ed.). (2001). The Merck Index-An Encyclopedia of chemicals, Drugs and Biologicals. 13th Edition, Whitehouse Station, NJ: Merck and Co., Inc. 2001. pp 1337)
PFA (2016am). Peter Fisk Associates, Silanols and aquatic systems, 404.105.003
Additional information
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