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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 202-895-5 | CAS number: 100-85-6
- 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)
- Endpoint:
- basic toxicokinetics, other
- Remarks:
- Toxicokinetic assessment of the substance based on the available data
- Type of information:
- other: expert statement
- Adequacy of study:
- key study
- Study period:
- Not applicable
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Theoretical assessment taking all currrently available relevant information into account, based on the REACH Guidance: Guidance on Information Requirements and Chemical Safety Assessment, Chapter R.7c Endpoint specific guidance. Since this is a theoretical assessment, the Klimisch value cannot be 1.
- Objective of study:
- other: Toxicokinetic assessment of the substance based on the available data
- Qualifier:
- according to guideline
- Guideline:
- other: ECHA Guidance on information requirements and chemical safety assessment. Chapter R.7c: Endpoint specific guidance
- Version / remarks:
- Version 3.0; June 2017
- Deviations:
- not applicable
- GLP compliance:
- no
- Type:
- absorption
- Results:
- For risk assessment purposes, 100% is used for oral, dermal and inhalation absorption
- Conclusions:
- A toxicokinetic assessment was performed based on the available data of the substance. Based on the physical/chemical properties of the substance, absorption factors for this substance are derived to be 100% (oral), 100% (inhalation) and 100% (dermal) for risk assessment purposes. The bioaccumulation potential is expected to be low.
Reference
Toxicokinetic assessment
Substances can enter the body via the gastrointestinal tract, the lungs, and the skin. In general, following oral administration, a compound is required to dissolve before adsorption can occur in the gastrointestinal tract. Benzyl trimethylammonium hydroxide (BTMAOH) is marketed as a 20% aqueous solution and as a 40 – 57% methanol solution. BTMAOH is highly soluble in water, therefore the substance will readily dissolve into the gastrointestinal fluids. Its low molecular weight may enable uptake via passive diffusion. However, the substance has a low partition coefficient which means that the substance is highly hydrophilic. This characteristic can hamper penetration through lipid membranes. BTMAOH dissociates in aqueous solutions in an OH-ion and a quaternary ammonium-ion. Due to the aqueous environment in the GI tract the substance will stay in ionized form. It is generally thought that ionized substances do not readily diffuse across biological membranes. Although its water solubility and its low molecular weight favour uptake, its low partition coefficient and its ionic form can hamper uptake. A toxicokinetic study with the benzyl trimethylammonium chloride (BMTAC), showed that uptake did not exceed 40% in rats and 15% in mouse in the GI tract (Sanders et al 1995, see below). Considering the quaternary ammonium ion is the same in BTMAOH, similar absorption rates could be expected. However, as BTMAOH is a corrosive it is likely to damage the GI tissues thereby increasing the absorption rate significantly. Therefore, for risk assessment purposes oral absorption of BTMAOH is set at 100%. Available oral toxicity data do not provide reason to deviate from the proposed oral absorption factor.
A toxicokinetic study with BTMAC showed wide distribution of the test item throughout the body in rat and mice (Sanders et al 1995, see below). Metabolism was minimal and most absorbed BTMAC was rapidly eliminated through the urine with no indication for bioaccumulation in tissues. BTMAOH is also expected to be widely distributed throughout the body based on its high water solubility and low molecular weight. Similar results in distribution are to be expected for BTMAOH compared to BTMAC as the structures contains the same cation.
The vapour pressure of pure BTMAOH was calculated to be low (9.5E-05 Pa) but considering BMTAOH is marketed as solution, aerosols could be formed. Therefore, it is assumed that BTMAOH can enter the respiratory tract. In case the substance reaches different regions of the lungs, high water solubility and low molecular weight in combination with the corrosive properties of BTMAOH will likely favour a high uptake in all lung regions. Therefore, for risk assessment purposes, the inhalation absorption of BTMAOH is set at 100%.
In case of skin contact with a solution of BTMAOH the quaternary ammonium ions will be binding to skin components thereby slowing absorption. In addition, the hydrophilicity of BTMAOH will limit the uptake via the skin. However, as BTMAOH is a corrosive the skin integrity will be negatively affected leading to an increased uptake. Once the skin surface is damaged, BTMAOH will be absorbed rapidly due to its low molecular weight and high water solubility. Based on the above data, for risk assessment purposes the dermal absorption of BTMAOH is set at 100%.
Reference: Sanders, J. M., Griffin, R. J., Burka, L. T., Matthews, H. B., Toxicokinetics of the cholinomimetic compound benzyltrimethylammonium chloride in the Male rat and mouse. Xenobiotica 1995; 25-3: 303-313.
Description of key information
A toxicokinetic assessment was performed based on the available data of the substance. Based on the physical/chemical properties of the substance, absorption factors for this substance are derived to be 100% (oral), 100% (inhalation) and 100% (dermal) for risk assessment purposes. The bioaccumulation potential is expected to be low.
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
- Absorption rate - oral (%):
- 100
- Absorption rate - dermal (%):
- 100
- Absorption rate - inhalation (%):
- 100
Additional information
Substances can enter the body via the gastrointestinal tract, the lungs, and the skin. In general, following oral administration, a compound is required to dissolve before adsorption can occur in the gastrointestinal tract. Benzyl trimethylammonium hydroxide (BTMAOH) is marketed as a 20% aqueous solution and as a 40 – 57% methanol solution. BTMAOH is highly soluble in water, therefore the substance will readily dissolve into the gastrointestinal fluids. Its low molecular weight may enable uptake via passive diffusion. However, the substance has a low partition coefficient which means that the substance is highly hydrophilic. This characteristic can hamper penetration through lipid membranes. BTMAOH dissociates in aqueous solutions in an OH-ion and a quaternary ammonium-ion. Due to the aqueous environment in the GI tract the substance will stay in ionized form. It is generally thought that ionized substances do not readily diffuse across biological membranes. Although its water solubility and its low molecular weight favour uptake, its low partition coefficient and its ionic form can hamper uptake. A toxicokinetic study with the benzyl trimethylammonium chloride (BMTAC), showed that uptake did not exceed 40% in rats and 15% in mouse in the GI tract (Sanders et al 1995, see below). Considering the quaternary ammonium ion is the same in BTMAOH, similar absorption rates could be expected. However, as BTMAOH is a corrosive it is likely to damage the GI tissues thereby increasing the absorption rate significantly. Therefore, for risk assessment purposes oral absorption of BTMAOH is set at 100%. Available oral toxicity data do not provide reason to deviate from the proposed oral absorption factor.
A toxicokinetic study with BTMAC showed wide distribution of the test item throughout the body in rat and mice (Sanders et al 1995, see below). Metabolism was minimal and most absorbed BTMAC was rapidly eliminated through the urine with no indication for bioaccumulation in tissues. BTMAOH is also expected to be widely distributed throughout the body based on its high water solubility and low molecular weight. Similar results in distribution are to be expected for BTMAOH compared to BTMAC as the structures contains the same cation.
The vapour pressure of pure BTMAOH was calculated to be low (9.5E-05 Pa) but considering BMTAOH is marketed as solution, aerosols could be formed. Therefore, it is assumed that BTMAOH can enter the respiratory tract. In case the substance reaches different regions of the lungs, high water solubility and low molecular weight in combination with the corrosive properties of BTMAOH will likely favour a high uptake in all lung regions. Therefore, for risk assessment purposes, the inhalation absorption of BTMAOH is set at 100%.
In case of skin contact with a solution of BTMAOH the quaternary ammonium ions will be binding to skin components thereby slowing absorption. In addition, the hydrophilicity of BTMAOH will limit the uptake via the skin. However, as BTMAOH is a corrosive the skin integrity will be negatively affected leading to an increased uptake. Once the skin surface is damaged, BTMAOH will be absorbed rapidly due to its low molecular weight and high water solubility. Based on the above data, for risk assessment purposes the dermal absorption of BTMAOH is set at 100%.
Reference: Sanders, J. M., Griffin, R. J., Burka, L. T., Matthews, H. B., Toxicokinetics of the cholinomimetic compound benzyltrimethylammonium chloride in the Male rat and mouse. Xenobiotica 1995; 25-3: 303-313.
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.