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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 700-368-9 | CAS number: 328-90-5
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1978
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 978
- Report date:
- 1978
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- no guideline available
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- bone marrow sampling time 6h after last dose instead of 18h; highest dose tested caused deaths; verification of bone marrow exposure to the test substance not specified.
- Principles of method if other than guideline:
- REFERENCES: [1] Boller, K., Schmid W. (1970) Humangenetik 11, 35; [2] Heddle J.A. (1973) Mutation Res. 18, 187; [3] Matter B., Schmid W. (1971) Mutation Res. 12, 417; [4] Schmid W. (1973) Agents and Actions, 3, 77; [5] Schmid W. (1975) Mutation Res. 31, 9; [6] Von Ledebur M., Schmid W. (1973) Mutation Res. 19, 109.
- GLP compliance:
- not specified
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- 2-hydroxy-4-(trifluoromethyl)benzoic acid
- EC Number:
- 700-368-9
- Cas Number:
- 328-90-5
- Molecular formula:
- C8H5F3O3
- IUPAC Name:
- 2-hydroxy-4-(trifluoromethyl)benzoic acid
- Test material form:
- solid
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CF-1
- Remarks:
- (CFLP, SPF)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Anglia Laboratory Animals (Alconbury, Huntingdon, UK)
- Age at study initiation: not specified
- Weight at study initiation: 19 - 23 g
- Assigned to test groups randomly: yes
- Fasting period before study: yes, overnight
- Housing: each group of 5 mice was kept in a plastic disposable cage and maintained in a controlled environment.
- Diet: 'Grain Harvester' Anglia Laboratory Animal Diet, ad libitum.
- Water: tap water, ad libitum.
- Acclimation period: 1 week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21 ± 2ºC
- Humidity (%): 50 ± 5% RH
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: 1% MC (methyl cellulose)
- Concentration of test material in vehicle: see experimental design in 'Any other information on materials and methods'.
- Dosing volume: 0.1 ml / 100 g bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: The test item was prepared as a suspension in 1% methylcellulose, by direct addition, using a high speed mixer.
- Duration of treatment / exposure:
- 30h
- Frequency of treatment:
- 2 equal doses separated by a 24-h interval
- Post exposure period:
- 6h
Doses / concentrationsopen allclose all
- Dose / conc.:
- 250 mg/kg bw/day (nominal)
- Dose / conc.:
- 500 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- mitomycin C;
- Route of administration: intraperitoneal injection
- Doses / concentrations: 14 mg/kg bw
Examinations
- Tissues and cell types examined:
- Polychromatic erythrocytes (PCE) from bone marrow.
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: preliminary studies, based on information provided, indicated that the LD50 of the test item is approximtely 400 mg/kg bw and that a top dosage of 1000 mg/kg bw would cause 1-2 deaths.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields):
- Treatment: rats were administered the test item by oral gavage at total doses of 250, 500, and 1000 mg/kg bw, as two equal doses separated by 24h (both administered after overnight fasting) of 10 ml/kg-bw dose volume.
DETAILS OF SLIDE PREPARATION:
- Following the last dose, the animals were observed for a further 6h before killing and all mortalities and signs of malreaction during the experiment were recorded. The animals were killed by cervical dislocation, the femurs dissected out and bone marrow smears prepared. The smears were fixed in methanol, deffated in xylene and stained with Giemsa.
METHOD OF ANALYSIS:
- The stained smears were examined by light microscopy. 2000 polychromatic erythrocites (PCEs) per mouse were scored for the frequency of micronucleated cells. - Evaluation criteria:
- In the micronucleus test, an individual trial is considered positive if the trend test P value is less than or equal to 0.025 or if the P value for any single dosed group is less than or equal to 0.025 divided by the number of dosed groups.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 400 - 1400 mg/kg bw.
- Clinical signs of toxicity in test animals: No toxic reactions were observed up to 600 mg/kg bw. At doses of 800 - 1400 mg/kg bw, hypopnoea was observed. Mortality data is summarized in table 1.
- High dose with and without activation: a dose of 1000 mg/kg bw was chosen as the highest dose that would be tolerated without evidence of study-limiting toxicity, relative to the duration of the study period.
RESULTS OF DEFINITIVE STUDY
- Clinical signs of toxicity in test animals: No reactions were observed up to 500 mg/kg bw. At 1000 mg/kg bw, hypopnoea was observed, and there were three mortalities between 24 and 30 hours after administration of the second dose.
- Induction of micronuclei (for Micronucleus assay): No significant increase observed at any dose tested. The negative control group gave a mean count of 2.6 micronucleated cells, within the laboratory historical value range. The mean micronucleated cell counts for groups treated at 250 and 500 mg/kg bw were comparable with the concurrent control value. The mean micronucleated cell count for the group treated at 1000 mg/kg bw was 2.7, slightly higher than the concurrent control. However, individual counts were within the historical range for negative controls. Therefore, the value was not considered statistically significant. The positive control gave a mean count of 92.7 micronucleated cells.
- Ratio of PCE/NCE (for Micronucleus assay): not examined.
Any other information on results incl. tables
Table 1. Preliminary toxicity study: mortality data.
Phase |
Group |
Material |
Total dosage over 24 h (mg/kg bw) |
Mortality ratio (no. deaths/no. dosed) |
Period during which deaths occurred (h) |
||||
♂ |
♀ |
Combined |
0 – 8 |
8 – 24 |
24 – 30 |
||||
I |
1a |
1% MC |
- |
0/2 |
0/2 |
0/4 |
|
|
|
2 |
UR1501 |
400 |
0/2 |
0/2 |
0/4 |
|
|
|
|
3 |
600 |
0/2 |
0/2 |
0/4 |
|
|
|
||
4 |
800 |
0/2 |
0/2 |
0/4 |
|
|
|
||
5 |
1000 |
0/2 |
0/2 |
0/4 |
|
|
|
||
6 |
1200 |
1/2 |
1/2 |
2/4 |
|
1 |
1 |
||
7 |
1400 |
1/2 |
1/2 |
2/4 |
|
|
2 |
||
II |
1b |
1% MC |
- |
0/5 |
0/5 |
0/10 |
|
|
|
8 |
UR1501 |
1000 |
1/5 |
2/5 |
3/10 |
|
|
3 |
|
9 |
1100 |
0/5 |
4/5 |
4/10 |
2 |
|
2 |
||
10 |
1200 |
5/5 |
3/5 |
8/10 |
6 |
|
2 |
||
11 |
1300 |
3/5 |
4/5 |
7/10 |
2 |
|
5 |
||
12 |
1400 |
5/5 |
3/5 |
8/10 |
5 |
|
3 |
Table 2. Main study: Group mean number of micronucleated cells per 2000 polychromatic erythrocytes per animal.
Group |
Material |
Total dosage over 24 h (mg/kg bw) |
Period during which deaths occurred (h) |
|
Mean |
Range |
|||
1 |
1% MC (vehicle control) |
- |
2.6 |
1 – 6 |
2 |
UR1501 |
250 |
2.2 |
1 – 5 |
3 |
500 |
2.1 |
0 – 6 |
|
4 |
1000 |
2.7 |
1 – 4 |
|
5 |
Mitomycin C (positive c.) |
14 |
92.7 |
71 – 126 |
Table. Number of micronucleated cells (mn) per 2000 polychromatic erythrocytes – individual values.
|
Material |
|
|
|
|
|
|
|
|
|
1% MC |
UR1501 |
Mitomicyn C |
||||||||
Group |
1 |
2 |
3 |
4 |
|
|||||
Dose (mg/kg) |
- |
250 |
500 |
1000 |
14 |
|||||
Sex |
Animal |
mn |
Animal |
mn |
Animal |
mn |
Animal |
mn |
Animal |
mn |
♂ |
1 |
1 |
6 |
3 |
11 |
2 |
16 |
D |
21 |
81 |
2 |
6 |
7 |
1 |
12 |
4 |
17 |
2 |
22 |
77 |
|
3 |
2 |
8 |
1 |
13 |
1 |
18 |
2 |
23 |
126 |
|
4 |
3 |
9 |
5 |
14 |
2 |
19 |
4 |
24 |
93 |
|
5 |
2 |
10 |
2 |
15 |
1 |
20 |
1 |
25 |
118 |
|
♀ |
26 |
2 |
31 |
3 |
36 |
2 |
41 |
4 |
46 |
77 |
27 |
2 |
32 |
2 |
37 |
2 |
42 |
D |
47 |
71 |
|
28 |
4 |
33 |
2 |
38 |
6 |
43 |
D |
48 |
94 |
|
29 |
1 |
34 |
1 |
38 |
1 |
44 |
4 |
49 |
102 |
|
30 |
3 |
35 |
2 |
40 |
0 |
45 |
2 |
50 |
88 |
D: animal died.
Table. Laboratory standard (historical) values in the period Feb 1972 – Feb 1978.
Negative control No. of experiments |
Total no. of animals examined |
Mean no. of micronucleated cells counted per 2000 PCE |
Range of individual counts of micronucleated cells per 2000 PCE per animal |
81 |
783 |
1.65 |
0 – 6 |
Applicant's summary and conclusion
- Conclusions:
- The test item was not mutagenic under test conditions.
- Executive summary:
An acute micronucleus study in bone marrow of CF-1 (CFLP, SPF) mice was performed for the test item, by a method similar to OECD 474 (non-GLP). Based on the results of a preliminary toxicity study were the LD50 was found to be around 400 mg/kg bw, five animals per sex per dose group were exposed to 250, 500 or 1000 mg/kg bw of test item in 1% methylcellulose by oral gavage, administered in two equal doses separated by a 24-hour resting period. Negative (vehicle, 1% aqueous methylcellulose) and positive (14 mg/kg bw Mitomicyn C by i.p. injection) controls were run in parallel. 6 hours after the last injection, the animals were killed by cervical dislocation, the femurs dissected out and and bone marrow spreads were prepared, air-dried, fixed using absolute methanol, defatted in xylene and stained with Giemsa. At termination, bone marrow analysis included assessment of the frequency of MN-PCE among 2,000 PCE per animal. All control values obtained were within the historical control range. No significant increase in the number of micronucleated PCE was observed at any dose tested, including the highest dose, which induced mortality. Since the results were clearly negative at all doses tested, the test item was not mutagenic under test conditions.
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.