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EC number: 203-929-1 | CAS number: 112-03-8
- 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 oral LD50 value of the test substance was determined to be 560 mg a.i./kg bw in rats, suggesting a moderate acute toxicity potential.
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:
- From January 03, 1996 to February 21, 1996
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.1 (Acute Toxicity (Oral))
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Hoe: WISKf (SPF71)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Hoechst aktiengesellschaft, Kastengrund, SPF breeding colony
- Age at study initiation: Approximately 7 wk (m) and 8 wk (f)
- Weight at study initiation: Mean: 185g (m) and 171g (f)
- Fasting period before study: Yes
- Housing: In fully air-conditioned rooms in macrolon cages on soft wood granulate in group of 5 animals
- Diet: Ssniff R/M-H (V 1534), ad libitum
- Water: Tap water, ad libitum
- Acclimation period: Atleast one day
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3°C
- Humidity (%): 50 ± 20% - Route of administration:
- oral: gavage
- Vehicle:
- water
- Remarks:
- Deionized
- Details on oral exposure:
- VEHICLE
- Concentration in vehicle: 6.3, 8, 12.5 and 20% in deionised water
- Justification for choice of vehicle: Test substance is soluble in water
MAXIMUM DOSE VOLUME APPLIED: 10 mL/kg bw
CLASS METHOD (if applicable)
- Rationale for the selection of the starting dose: Dose range finding study - Doses:
- 800 and 2,000 mg/kg bw for males and 630, 800, 1,250 and 2,000 mg/kg bw
- No. of animals per sex per dose:
- 5 per sex per dose
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14d
- Frequency of observations and weighing: Symptoms and lethality were recorded twice every day, on weekends and public holiday only once. weighing was done weekly
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight,organ weights, histopathology - Statistics:
- The LD50 and the equation of the probit line were established in female animals on the basis of the lethality rates by probit analysis.
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- ca. 702.5 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: equivalent to 560.5 mg a.i./kg bw
- Key result
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- > 800 - < 2 000 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: equivalent to >638 to <1596 mg a.i./kg bw
- Mortality:
- Yes, although in males there was no mortality at 800 mg/kg bw, all animals died at 2,000 mg/kg bw. In females, only 2 and 3 animals survived at 630 and 800 mg/kg bw, respectively. At 1,250 and 2,000 mg/kg bw, all females died.
- Clinical signs:
- other: Decreased spontaneous activity, squatting posture, narrowed palpebrae fissures and irregular respiration. Also, stupor was observed only in the animals of the 2,000 mg/kg bw group. One female animal of the 800 mg/kg bw group showed blood encrusted lid mar
- Gross pathology:
- Macroscopic examination of the dead animals:
Stomach: Full of clear fluid, full of gas, detachment of the mucosa, petechial bleeding
Intestinal tract: Full of yellowish mucous, full of clear fluid, detachment of the mucosa, full of reddish mucosa
The animals killed at the end of the observation period showed macroscopically visible changes. - Conclusions:
- Under the study conditions, the LD50 values for the female and male Wistar rats were determined to be 702.5 and >800 to <2000 mg/kg bw, respectively (equivalent to 560.5 and >638 to <1596 mg a.i./kg bw, respectively).
- Executive summary:
A study was conducted to determine the oral acute toxicity of the test substance, C18 TMAC (79.8% active) according to OECD Guideline 401 and EU Method B.1, in compliance with GLP. The experiment was performed in Wistar rats. The test substance was administered as a single dose to 5 female rats per group at 630, 800, 1250 and 2000 mg/kg bw (equivalent to 503, 638, 998 and 1596 mg a.i./kg bw) and to 5 males rats per group at doses of 800 and 2000 mg/kg bw (equivalent to 638 and 1596 mg a.i./kg bw, after which animals were examined for 14 days. Examinations performed were mortality, body weights, clinical signs and gross necropsy for any macroscopic abnormalities. In males, there was no mortality at 800 mg/kg bw, however all animals died at 2000 mg/kg bw. In females, only 2 and 3 animals survived at 630 and 800 mg/kg bw respectively. At 1250 and 2000 mg/kg bw, all females died. Females, therefore, appeared to be more susceptible to the effects of treatment than males. Decreased spontaneous activity, squatting posture, narrowed palpebrae fissures and irregular respiration were recorded. Also, stupor was observed only in the animals of the 2000 mg/kg bw group. One female animal of the 800 mg/kg bw group showed blood encrusted lid margin on Day 6 of the study. All clinical signs were reversible at Day 8 of the study. No effects were seen on the body weight. The animals killed at the end of the observation period showed macroscopically visible changes. Under the study conditions, the LD50 values for the female and male Wistar rats were determined to be 702.5 and >800 to <2000 mg/kg bw, respectively (equivalent to 560.5 and >638 to <1596 mg a.i./kg bw, respectively) (Jensch, 1996).
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 560.5 mg/kg bw
- Quality of whole database:
- Guideline compliant study
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because the substance is classified as corrosive to the skin
- other:
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Clinical signs:
- other:
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because the substance is classified as corrosive to the skin
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Oral:
A study was conducted to determine the oral acute toxicity of the test substance, C18 TMAC (79.8% active) according to OECD Guideline 401 and EU Method B.1, in compliance with GLP. The experiment was performed in Wistar rats. The test substance was administered as a single dose to 5 female rats per group at 630, 800, 1250 and 2000 mg/kg bw (equivalent to 503, 638, 998 and 1596 mg a.i./kg bw) and to 5 males rats per group at doses of 800 and 2000 mg/kg bw (equivalent to 638 and 1596 mg a.i./kg bw, after which animals were examined for 14 days. Examinations performed were mortality, body weights, clinical signs and gross necropsy for any macroscopic abnormalities. In males, there was no mortality at 800 mg/kg bw, however all animals died at 2000 mg/kg bw. In females, only 2 and 3 animals survived at 630 and 800 mg/kg bw respectively. At 1250 and 2000 mg/kg bw, all females died. Females, therefore, appeared to be more susceptible to the effects of treatment than males. Decreased spontaneous activity, squatting posture, narrowed palpebrae fissures and irregular respiration were recorded. Also, stupor was observed only in the animals of the 2000 mg/kg bw group. One female animal of the 800 mg/kg bw group showed blood encrusted lid margin on Day 6 of the study. All clinical signs were reversible at Day 8 of the study. No effects were seen on the body weight. The animals killed at the end of the observation period showed macroscopically visible changes. Under the study conditions, the LD50 values for the female and male Wistar rats were determined to be 702.5 and >800 to <2000 mg/kg bw, respectively (equivalent to 560.5 and >638 to <1596 mg a.i./kg bw, respectively) (Jensch, 1996).
Inhalation:
In accordance with Annex VII, Section 8.5, Column 2, additional acute toxicity study for inhalation route does not need to be conducted because the substance is classified as corrosive to the skin. Further, due to its low vapour pressure (VP = 2.9E-6 at 25°C, which is below cutoff of 0.01 Pa as per the ECHA R.7a guidance), it is unlikely that the test substance will form inhalable dust, mist or fumes when handled and used in solid form. In case inhalable forms of the substance (either pure or in aqueous solutions) are created under particular conditions (e.g., spraying, elevated temperature/pressure), appropriate risk management measures such as closed systems, exhaust ventilation or wearing of respirators are implemented to control exposure. Under such conditions, the risk to humans following inhalation exposure can be considered minimal and further testing involving vertebrate animals may also be omitted, in accordance with Annex XI, section 1.2 (weight of evidence) of the REACH regulation.
Dermal:
In accordance with Annex VII, Section 8.5, Column 2, additional acute toxicity study for dermal route does not need to be conducted because the substance is classified as corrosive to the skin (Category 1C).
Justification for classification or non-classification
Based on the oral LD50 value, the test substance warrants an ‘Acute Tox. 4; H302: harmful if swallowed’ classification according to EU CLP criteria (Regulation EC 1272/2008). In addition, for the inhalation route, although C18 TMAC is classified to be corrosive (see section 5.3) and this drives its mechanism of action of toxicity, its inherent low vapour pressure prohibits the occurrence of respiratory irritation or corrosion by vapour. Therefore, it does not warrant an additional labelling as: EUH071 — ‘Corrosive to the respiratory tract’ according to EU CLP criteria (Regulation EC 1272/2008).
Further, the available data does not show indication that classification for STOT-SE cat 1 or 2 is indicated. For STOT-SE Cat 3: C18 TMAC or QAS substances are not narcotic.
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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