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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 242-177-9 | CAS number: 18297-63-7
- 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
Acute oral toxicity (OECD 420, rat, f): LD50 = > 300 < 2000 mg/kg bw
Acute inhalation toxicity (OECD 433, rat, m/f): LC50 > 5.30 mg/L (aerosol)
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 23 Jul - 20 Aug 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 420 (Acute Oral Toxicity - Fixed Dose Method)
- Version / remarks:
- adopted in 2001
- Deviations:
- yes
- Remarks:
- On 3 days the temperature was approx. 20 - 27 °C instead of 19 - 25 °C; the age of the animals was 7 - 12 weeks instead of 8 - 12 weeks
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.1 bis (Acute Oral Toxicity - Fixed Dose Procedure)
- Version / remarks:
- adopted in 2008
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Hessisches Ministerium für Umwelt, Klimaschutz, Landwirtschaft und Verbraucherschutz, Wiesbaden, Germany
- Test type:
- fixed dose procedure
- Limit test:
- no
- Specific details on test material used for the study:
- Dose calculation was adjusted to purity with a correction factor of 1.03.
- Species:
- rat
- Strain:
- Wistar
- Remarks:
- Han TM
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Envigo RMS B.V., Inc, AD Horst, The Netherlands
- Females nulliparous and non-pregnant: yes
- Age at beginning of treatment: 7 - 12 weeks
- Weight at beginning of treatment: 159.7 - 197.9 g
- Fasting period before study: The animals were fasted over night before treatment, with constant ad libitum access to drinking water.
- Housing: In groups of 5 in Makrolon Type IV cages with wire mesh top and granulated soft wood bedding.
- Diet: certified 2018C Teklad Global 18% protein rodent diet, ad libitum
- Water: tap water, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2
- Humidity (%): 45 - 65
- Photoperiod (hrs dark / hrs light): 12 / 12
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- VEHICLE
- Concentration in vehicle: 30 and 200 mg/mL
- Amount of vehicle: 10 mL/kg bw
- Justification for choice of vehicle: The test item was not stable in water due to hydrolysis.
MAXIMUM DOSE VOLUME APPLIED: 10 mL/kg bw - Doses:
- Pilot study: 300 and 2000 mg/kg bw
Main study: 300 mg/kg bw - No. of animals per sex per dose:
- Pilot study: 1 female per dose
Main study: 4 females - Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations: Clinical observations and inspections for morbidity / mortality were performed at least 3 times within the first six hours after application (i.e., 30 minutes and 1 hour, 2 hours and 4 hours after dosing), thereafter at least once daily for 14 days. All surviving animals were observed for 14 days after dosing.
- Frequency of weighing: Body weights were recorded on Day 0 (prior to dosing), Day 7 and 14.
- Necropsy of survivors performed: Yes, gross necropsy was performed on all animals that died or were humanely killed during the study and at the end of the in-life part. Any macroscopic abnormalities were recorded. - Statistics:
- No statistical analysis was performed.
- Preliminary study:
- In the sighting study, two single females each were dosed at 300 and 2000 mg/kg bw/day. The animal dosed at 2000 mg/kg bw/day had to be humanely sacrificed 4 h after application due to moribund condition and unconsciousness. The animals showed clinical signs of toxicity starting 30 minutes after dosing, including decreased activity, ataxia, decreased respiration rate, sunken flanks, piloerection, lethargy, and laboured respiration. At macroscopical examination, a full urinary bladder was observed. Based on these findings, the main study was conducted at 300 mg/kg bw.
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- > 300 - < 2 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- Pilot study:
300 mg/kg bw: 0/1 females died
2000 mg/kg bw: 1/1 females was sacrificed for humane reasons 4 hours post-dosing.
Main study: No mortality occured during the study period. - Clinical signs:
- other: Pilot study: 300 mg/kg bw: 1/1 females showed piloerection, hunched posture, decreased activity and a decreased respiration rate within 4 hours post-administration. The effects were fully reversible by study Day 1. 2000 mg/kg bw: 1/1 females showed decr
- Gross pathology:
- Pilot study:
300 mg/kg bw: There were no abnormal findings at gross necropsy.
2000 mg/kg bw: The animal sacrificed for humane reasons was found to have a full urinary bladder.
Main study: 3 - 4 red nodules above the thymus were noted in 1/4 females, being indicative of enlarged lymph nodes. The effect was not attributed to treatment. There were no findings in the remaining animals. - Interpretation of results:
- other: Acute Oral 4, H302 according to Regulation (EC) No. 1272/2008
- Conclusions:
- In this acute oral toxicity study in rats a LD50 value between 300 - 2000 mg/kg bw was determined.
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- > 300 - < 2 000 mg/kg bw
- Quality of whole database:
- The available information comprises an adequate and reliable study, and is thus sufficient to fulfil the standard information requirements set out in Annex VII, 8.5, of Regulation (EC) No. 1907/2006.
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 01 Apr - 12 May 2020
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 433 (Acute Inhalation Toxicity: Fixed Concentration Procedure)
- Version / remarks:
- adopted in 2018
- Deviations:
- no
- GLP compliance:
- yes
- Test type:
- fixed concentration procedure
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Remarks:
- RccHan®:WIST
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Envigo RMS Ltd. (UK)
- Age at study initiation: 8 - 12 weeks
- Weight at study initiation: 242 - 295 g (males) and 185 - 191 g (females)
- Fasting period before study: no
- Housing: Individually during the sighting study and in groups of 5 during the main study. The cages were made of a polycarbonate body with a stainless steel mesh lid. Autoclaved softwood bark-free fiber was used as bedding.
- Diet: Teklad 2014C Diet, ad libitum
- Water: potable water from the public water supply, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24
- Humidity (%): 40 - 70
- Photoperiod (hrs dark / hrs light): 12 / 12 - Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- nose only
- Vehicle:
- air
- Mass median aerodynamic diameter (MMAD):
- 2 - 2.2 µm
- Geometric standard deviation (GSD):
- 2.25 - 2.64
- Remark on MMAD/GSD:
- The Mass Median Aerodynamic Diameter (MMAD) ± Geometric Standard Deviation (GSD) was 2.1 ± 2.25 µm at 1 mg/L (sighting study) and 2.0 ± 2.34 µm (sighting study) and 2.2 ± 2.64 µm (main study) at 5 mg/L air, respectively.
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: The exposure apparatus was a Flow through nose-only chamber (ADG Developments Ltd, Hitchin, Hertfordshire, England) with an aluminum alloy construction comprising a base unit, one animal exposure section with 20 exposure ports, and a top section.
- Exposure chamber volume: approximately 30 L
- Method of holding animals in test chamber: plastic nose-only restraint tube
- Source and rate of air (airflow): The aerosol was generated by Wright Dust Feed Mechanism, which produces and maintains test atmospheres containing dust by suspending material scraped from the surface of compressed powder in a stream of dry air. The inlet airflow was 44 L/min.
- Method of particle size determination: The particle size distribution was characterized twice during each exposure period. The aerosol samples were drawn with a flow of 2 L/min. Particle size distribution was determined by cascade impaction using a Marple 290 Series Personal Cascade Impactor (Andersen Instruments, Smyrna, Georgia, USA). Amounts of test item collected were measured gravimetrically. Subsequently the Mass Median Aerodynamic Diameter (MMAD) and the Geometric Standard Deviation (GSD) were derived.
- Treatment of exhaust air: Extract airflow was drawn by in-house vacuum system and filtered locally. The flow was 45 - 46 L/min.
- Mean temperature in air chamber: 19.8 ± 0.65 °C (1 mg/L, sighting study), 19.4 ± 0.22 °C (5 mg/L, sighting study) and 19.7 ± 0.21 °C (5 mg/L, main study).
- Humidity in air chamber: 9.4 ± 0.88% (1 mg/L, sighting study), 14.8 ± 2.42% (5 mg/L, sighting study) and 16.8 ± 1.23% (5 mg/L, main study).
TEST ATMOSPHERE
- Brief description of analytical method and equipment used: Aerosol samples were collected by using a glass microfiber filter held in an open face filter holder. Five samples were collected during each exposure.
- Samples taken from breathing zone: yes - Analytical verification of test atmosphere concentrations:
- yes
- Remarks:
- gravimetric
- Duration of exposure:
- 4 h
- Concentrations:
- Sighting study:
1.02 ± 0.020 and 5.04 ± 0.283 mg/L air (analytical concentrations)
1.34 and 6.58 mg/L air (nominal concentrations)
Main study:
5.30 ± 0.225 mg/L air (analytical concentration)
6.34 mg/L air (nominal concentration) - No. of animals per sex per dose:
- Sighting study: 1 male and 1 female per step (2 steps)
Main study: 5 males - Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 8 - 10 days (sighting study) and 15 days (main study).
- Frequency of observations: Throughout the study all cages were checked at least twice daily, once in the morning and again towards the end of the normal working day, for dead or moribund animals. The animals were observed for clinical signs prior to dosing, at hourly intervals during exposure, 1 and 2 hours after exposure and as late as possible in the working day of exposure. Thereafter, the animals were inspected visually at least twice daily for evidence of ill-health or reaction to treatment. Any deviation from normal was recorded at the time in respect of nature and severity, date and time of onset, duration and progress of the observed condition, as appropriate. Detailed physical examinations were performed weekly.
- Frequency of weighing: In the sighting study, rats were weighed at least once during the week prior to exposure, on Day 1 (prior to dosing) and on Days 2, 4 and 10. In the main study, rats were weighed at least once during the week prior to exposure, on Day 1 (prior to dosing) and on Days 2, 4, 8 and 15.
- Necropsy of survivors performed: Yes, all main study animals were subjected to a macroscopic examination which consisted of opening the cranial, thoracic and abdominal cavities. The macroscopic appearance of all examined organs was recorded. Tissues were discarded following necropsy. Special attention was paid to the lungs and respiratory tract for signs of irritancy and local toxicity during necropsy observation. - Statistics:
- No statistical analysis was performed.
- Preliminary study:
- In the sighting study, each one male and one females were dosed at 1 mg/L air, corresponding to an analytical concentration of 1.02 ± 0.020 mg/L air. Evident toxicity was not observed therefore a further one male and one female received a single 4-hour nose only exposure of the test item at the target concentration of 5 mg/L, corresponding to an analytical concentration of 5.04 ± 0.283 mg/L air, and observed for seven days. The results of this exposure determined the starting exposure level for the main exposure.
- Key result
- Sex:
- male
- Dose descriptor:
- LC50
- Effect level:
- > 5.3 mg/L air (analytical)
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Mortality:
- No mortality occurred during the study period.
- Clinical signs:
- other: Please refer to "Any other information on results incl. tables".
- Body weight:
- A slight loss in mean body weight was noted in the animals one day following exposure, which was considered to be a consequence of food and water removal during exposure. The finding was considered as normal body weight variation and therefore not attributed to treatment. For details please refer to Table 2 under "Any other information on results incl tables".
- Gross pathology:
- Necropsy revealed no substance-related findings. 1/5 males was observed to have small testes and epididymides bilaterally. The findings were reported to be occasionally observed in inhalation studies due to the method of restraint and duration of exposure and therefore not attributed to treatment.
- Interpretation of results:
- other: CLP/EU GHS criteria not met, no classification required according to Regulation (EC) No. 1272/2008
- Conclusions:
- CLP: not classified
Reference
Clinical signs:
After dosing, powder in the nose was observed in 4/5 males and an unsteady gait was noted in 5/5 males one hour after exposure. The findings had resolved in 2/5 males within 2 hours after exposure and by study Day 5 in the remaining animals. Decreased activity was seen in 4/5 males, with a flattened posture seen in 3/5 males in Day 1. Both signs resolved in all animals by study Day 2.
Piloerection and hunched posture were noted in 2/5 males 1 and 2 hours after exposure. Salivation was noted in 1/5 animals, which further showed closed bilateral eyes 1 hour after exposure and slow breathing 2 hours after exposure. All signs had resolved by study Day 2.
Clinical signs associated with the dosing procedure included wet fur (1/5) and staining of the nose (1/5) for some animals, these were considered to be a consequence of tube restraint during exposure.
Body weight development:
Table 2: Mean body weights
Day P19 | Day 1 | Day 2 | Day 4 | Day 8 | Day 15 | |
Mean | 275.2 | 282 | 278.8 | 281.2 | 288.4 | 297.8 |
SD | 9.44 | 10.54 | 10.28 | 11.54 | 14.33 | 14.18 |
% control | 100.00 | 102.47 | 101.31 | 102.18 | 104.80 | 108.21 |
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LC50
- Value:
- > 5.3 mg/L air
- Quality of whole database:
- The available information comprises an adequate and reliable study, and is thus sufficient to fulfil the standard information requirements set out in Annex VIII, 8.5, of Regulation (EC) No. 1907/2006.
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Acute oral toxicity:
N,N-Bis-(trimethylsilyl)urea was tested for acute oral toxicity according to OECD guideline 420 (fixed dose procedure) and in compliance with GLP (ICCR-Roßdorf GmbH, 2020a). The test item was dissolved in corn oil and administered by oral gavage to female Wistar rats.
A sighting study was performed prior to the main study, in which doses of 300 and 2000 mg/kg bw were administered to one female each. The animal dosed at 2000 mg/kg bw showed systemic effects and had to be sacrificed for humane reason, therefore the main study was conducted at 300 mg/kg bw. In the main study, 4 additional females were administered 300 mg/kg bw at a constant dose volume of 10 mL/kg bw and observed for a time period of 14 days. Mortality, clinical sings of toxicity and individual body weights were recorded. At terminal sacrifice, all animals were subjected to gross necropsy.
No mortality occurred at 300 mg/kg bw. Clinical signs of toxicity comprised decreased activity, hunched posture, piloerection, lethargy and laboured respiration within 24 hours post-dosing. The effects were fully reversible by study Day 2. There were no treatment-related effects on body weight development. At scheduled necropsy, 3 - 4 red nodules above the thymus were noted in 1/4 females, being indicative of enlarged lymph nodes. The effect was not attributed to treatment.
Under the tested conditions, the acute oral LD50 in female rats was established to be within the range of > 300 and < 2000 mg/kg bw.
Acute inhalation toxicity:
In an acute inhalation toxicity study according to OECD guideline 433 (fixed concentration procedure) and in compliance with GLP (Covance Laboratories Ltd., 2020a), Wistar rats were exposed to aerosols of the test item by nose-only application. A sighting study with each 1 male and 1 female animal dosed at nominal concentrations of 1 and 5 mg/L air (achieved concentrations of 1.02 and 5.04 mg/L air) was performed to select a suitable concentration for the main inhalation study. The mass median aerodynamic diameter (MMAD) and geometric standard deviation (GSD) in the sighting study were 2.1 ± 2.25 µm at 1 mg/L and 2.0 ± 2.34 µm at 5 mg/L.
In the main study, a group of 5 male rats was exposed for 4 hours to an aerosol concentration of 5.30 ± 0.225 mg/L air. The MMAD and GSD was 2.2 ± 2.64 µm. During exposure and thereafter, the animals were observed for clinical signs of toxicity and mortality. During a 14-days observation period, the animals were inspected for general health and mortality and individual body weights were recorded on Day 1 (prior to dosing) and on Days 2, 4, 8 and 15. At terminal sacrifice, all animals were subjected to gross macroscopical examination.
No mortality was observed throughout the study. After dosing, powder in the nose was observed in 4/5 males and an unsteady gait was noted in 5/5 males one hour after exposure, which remained up to 5 days after exposure. Decreased activity was seen in 4/5 males, with a flattened posture seen in 3/5 males in Day 1. Both signs resolved in all animals by study Day 2. Piloerection and hunched posture were noted in 2/5 males 1 and 2 hours after exposure. Salivation was noted in 1/5 animals, which further showed closed bilateral eyes 1 hours after exposure and slow breathing 2 hours after exposure. All signs had resolved by study Day 2. Clinical signs associated with the dosing procedure included wet fur in 1/5 animals and staining of the nose in 1/5 animals and were considered to be a consequence of tube restraint during exposure.
A slight loss in mean body weight was noted in the animals one day following exposure, which was considered to be a consequence of food and water removal during exposure. The finding was considered as normal body weight variation and therefore not attributed to treatment.
At necropsy, 1/5 males was observed to have small testes and epididymides bilaterally. The observation was considered to be occasionally observed and not attributed to treatment.
Under the tested conditions, the acute inhalation LC50 in male rats was established to be > 5.30 mg/L air.
Justification for classification or non-classification
The available data on acute oral toxicity of the test substance meet the criteria for classification as Acute Tox. 4 (H302) according to Regulation (EC) No. 1272/2008. The available data on acute inhalation toxicity do not meet the criteria for classification according to Regulation (EC) No. 1272/2008, and are therefore conclusive but not sufficient for classification.
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.