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EC number: 257-407-3 | CAS number: 51772-85-1
- 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
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
There are no data on the toxicokinetics of 3-[tris(acetoxy)silyl]propyl methacrylate.
The following summary has therefore been prepared based on validated predictions of the physicochemical properties of the substance itself and its hydrolysis products and using this data in algorithms that are the basis of many computer-based physiologically based pharmacokinetic or toxicokinetic (PBTK) prediction models. Although these algorithms provide a numerical value, for the purposes of this summary only qualitative statements or comparisons will be made.
The main input variable for the majority of these algorithms is log Kow so by using this, and other where appropriate, known or predicted physicochemical properties of 3-[tris(acetoxy)silyl]propyl methacrylate or its hydrolysis products, reasonable predictions or statements can be made about their potential absorption, distribution, metabolism and excretion (ADME) properties.
3-[tris(acetoxy)silylpropyl methacrylate hydrolyses in contact with water (predicted hydrolysis half-lives <1 minute at 25oC and pH 4, 7 and 9), generating 3-(trihydroxysilyl)propyl methacrylate and acetic acid. Human exposure can occur via the inhalation or dermal routes. Relevant inhalation and dermal exposure would be to the hydrolysis products, due to the rapid hydrolysis rate.
The toxicokinetics of acetic acid have been reviewed in other major reviews (OECD SIDS, 2005) and are not considered further here.
Absorption
Oral
Significant oral exposure is not expected for this corrosive substance.
When oral exposure takes place it can be assumed, except for the most extreme of insoluble substances, that uptake through intestinal walls into the blood occurs. Uptake from intestines can be assumed to be possible for all substances that have appreciable solubility in water or lipid. Other mechanisms by which substances can be absorbed in the gastrointestinal tract include the passage of small water-soluble molecules (molecular weight up to around 200) through aqueous pores or carriage of such molecules across membranes with the bulk passage of water (Renwick, 1993).
The hydrolysis product, 3-(trihydroxysilyl)propyl methacrylate has a favourable molecular weight (206.27) and water solubility for absorption so should oral exposure occur then systemic exposure is likely.
Dermal
Dermal exposure would be to the hydrolysis products. Corrosive effects would be predominant due to the properties of the acetic acid.
The fat solubility and therefore potential dermal penetration of the hydrolysis product 3-(trihydroxysilyl)propyl can be estimated by using the water solubility and log Kow values. Substances with log Kow values between 1 and 4 favour dermal absorption (values between 2 and 3 are optimal) particularly if water solubility is high.
For the hydrolysis product, 3-(trihydroxysilyl)propyl methacrylate, although it is highly soluble (predicted solubility 1E+06 mg/L), the log Kow value (-0.9) indicates it is not likely to be sufficiently lipophilic to cross the stratum corneum and therefore dermal absorption into the systemic circulation is likely to be minimal. However, as the registered substance is corrosive to skin, due to the production of acetic acid, damage to the skin may increase the potential penetration.
Inhalation
There is a Quantitative Structure-Property Relationship (QSPR) to estimate the blood:air partition coefficient for human subjects as published by Meulenberg and Vijverberg (2000). The resulting algorithm uses the dimensionless Henry coefficient and the octanol:air partition coefficient (Koct:air) as independent variables.
For the hydrolysis product 3-(trihydroxysilyl)propyl methacrylate the predicted blood:air partition coefficient is approximately 5E+11:1 meaning that significant uptake in to the systemic circulation is likely. However, the high water solubility may result in some of the hydrolysis product being retained in the mucus of the lungs so once hydrolysis has occurred, absorption is likely to slow down.
Distribution
For blood:tissue partitioning a QSPR algorithm has been developed by DeJongh et al. (1997) in which the distribution of compounds between blood and human body tissues as a function of water and lipid content of tissues and the n-octanol:water partition coefficient (Kow) is described. No information on the log Kowand water solubility of the parent compound are available, due to the rapid hydrolysis which takes place.
For the hydrolysis product 3-(trihydroxysilyl)propyl methacrylate, distribution into the main body compartments is predicted to be minimal.
Table: Tissue:blood partition coefficients
|
Log Kow |
Kow |
Liver |
Muscle |
Fat |
Brain |
Kidney |
3-[tris(acetoxy)silyl]propyl methacrylate |
n/a |
n/a |
n/a |
n/a |
n/a |
n/a |
n/a |
3-(trihydroxysilyl)propyl |
-0.9 |
0.13 |
0.6 |
0.7 |
0.0 |
0.7 |
0.8 |
Metabolism
There are no data on the metabolism of 3-[tris(acetoxy)silyl]propyl methacrylate. However, it will hydrolyse immediately when in contact with moisture to form acetic acid and 3-(trihydroxysilyl)propyl methacrylate. Genetic toxicity tests in vitro showed no observable differences in effects with and without metabolic activation.
Excretion
A determinant of the extent of urinary excretion is the soluble fraction in blood. QPSRs as developed by DeJongh et al.(1997) using log Kow as an input parameter, calculate the solubility in blood based on lipid fractions in the blood assuming that human blood contains 0.7% lipids.
Using
the algorithm, the soluble fraction of the hydrolysis product
3-(trihydroxysilyl)propyl
methacrylate in blood is >99% meaning that once absorbed the hydrolysis
product is likely to be eliminated via the kidneys in urine and
accumulation is unlikely.
References
Renwick A. G. (1993) Data-derived safety factors for the evaluation of food additives and environmental contaminants.Fd. Addit. Contam.10: 275-305.
Meulenberg, C.J. and H.P. Vijverberg, Empirical relations predicting human and rat tissue:air partition coefficients of volatile organic compounds. Toxicol Appl Pharmacol, 2000. 165(3): p. 206-16.
DeJongh, J., H.J. Verhaar, and J.L. Hermens, A quantitative property-property relationship (QPPR) approach to estimate in vitro tissue-blood partition coefficients of organic chemicals in rats and humans. Arch Toxicol, 1997.72(1): p. 17-25.
OECD (2005): SIDS Initial Assessment Report for SIAM 21, Washington DC, USA, 18-21 October 2005, Methyltriacetoxysilane, CAS 4253-34-3
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