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EC number: 218-485-4 | CAS number: 2162-73-4
- 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
Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- chronic toxicity: inhalation
- Remarks:
- Carcinogenicity study
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- weight of evidence
- Justification for type of information:
- Please refer to Read-across statement in section 13
Data source
Materials and methods
Test material
- Reference substance name:
- 2,4,6-triisopropyl-m-phenylene diisocyanate
- EC Number:
- 218-485-4
- EC Name:
- 2,4,6-triisopropyl-m-phenylene diisocyanate
- Cas Number:
- 2162-73-4
- Molecular formula:
- C17H22N2O2
- IUPAC Name:
- 2,4-diisocyanato-1,3,5-tris(propan-2-yl)benzene
- Test material form:
- liquid
Constituent 1
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- No exposure-related signs occurred during the study. At termination of the study total percentage deaths were 65% in controls, 67% low dose, 71% high dose males & 68% in controls, 75% low dose, 64% high dose females.
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- No exposure-related signs occurred during the study. At termination of the study total percentage deaths were 65% in controls, 67% low dose, 71% high dose males & 68% in controls, 75% low dose, 64% high dose females.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- in all groups during the main part of the study. Significantly less weight gain in the 0.15 ppm group in both sexes in the first 12 weeks of exposure. Weight increases between weeks 12 and 108 show comparable weight gains for all groups.
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- No treatment-related changes in haematological parameters were recorded.
- Clinical biochemistry findings:
- no effects observed
- Description (incidence and severity):
- No treatment-related changes in blood biochemical parameters were recorded.
- Urinalysis findings:
- no effects observed
- Description (incidence and severity):
- No treatment-related changes in urinary parameters were recorded.
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- The statistical analysis of the organ weights of the animals from interim and terminal kills did not reveal treatment-related differences.
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- The examination of the tissues did not reveal any evidence of treatment-related effects. Macroscopically no changes were seen in the upper respiratory tract.
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- Microscopic evaluation of the tissues revealed some alterations in all groups which were considered incidental and not treatment-related. It should, however, be noted that histopathology of the nasal turbinates is still in progress.
- Histopathological findings: neoplastic:
- no effects observed
- Description (incidence and severity):
- Statistical evaluation demonstrated no treatment-related effect on the incidence of tumours, their multiplicity or malignancy.
- Details on results:
- CLINICAL SIGNS AND MORTALITY
No exposure-related signs occurred during the study. At termination of the study (at week 110 for males and at week 108 for females) total percentage deaths were 65% in controls, 67% low dose, 71% high dose males and 68% in controls, 75% low dose, 64% high dose females. Statistical analysis indicated that TDI did not significantly affect mortality.
BODY WEIGHT AND WEIGHT GAIN
Body weight gain was similar in all groups during the main part of the study. There was, however, significantly less weight gain in the 0.15 ppm group in both sexes in the first 12 weeks of exposure. The weight increases for the periods between weeks 12 and 108 show comparable weight gains for all groups.
OPHTHALMOSCOPIC EXAMINATION
No effects reported.
HAEMATOLOGY
No treatment-related changes in haematological parameters were recorded.
CLINICAL CHEMISTRY
No treatment-related changes in blood biochemical parameters were recorded.
URINALYSIS
No treatment-related changes in urinary parameters were recorded.
ORGAN WEIGHTS
The statistical analysis of the organ weights of the animals from interim and terminal kills did not reveal treatment-related differences.
GROSS PATHOLOGY
At necropsy the examination of the tissues from control and TDI-exposed animals did not reveal any evidence of treatment-related effects. Macroscopically no changes were seen in the upper respiratory tract.
HISTOPATHOLOGY: NON-NEOPLASTIC
Microscopic evaluation of the tissues revealed some alterations in all groups which were considered incidental and not treatment-related. It should, however, be noted that histopathology of the nasal turbinates is still in progress.
HISTOPATHOLOGY: NEOPLASTIC (if applicable)
Statistical evaluation demonstrated no treatment-related effect on the incidence of tumours, their multiplicity or malignancy.
Effect levels
- Dose descriptor:
- NOAEC
- Effect level:
- 0.15 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: not specified
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Range-finding study:
Male rats of both the Fisher 344 and Sprague-Dawley strain exposed to 0.1 or 0.3 ppm TDI showed a slight but significant reduction in body weight gain. A greater incidence of sneezing occurred in the Sprague-Dawley males suggesting slight respiratory irritation. No adverse effects were observed in the mouse and hamster study.
Rats did not exhibit changes in the lower respiratory tract (histopathology of upper respiratory tract in progress) nor was there any trend of increased mortality in any group. Rats exposed at 0.15 ppm had significantly less increase in weight, only in the first 12 weeks of the study. No specific target tissue has been identified. The tumour pattern in the rat study was similar in the control and in the treated groups and corresponded to historical data. The study demonstrated no evidence of any neoplastic response. These results are supported by tests on mutagenicity. There was no evidence of a mutagenic response in vivo as demonstrated by the results of a micronucleus test on rats and mice exposed for four weeks to TDI at exposure concentrations up to and including 0.15 ppm. As far as the incomplete rat study can be interpreted, levels which cause no primary irritative effect also do not result in any other effect of toxicological significance. As a result of these studies the current occupational exposure levels are not considered to represent a serious health hazard. The possible sensitization to TDI, however, needs special attention.
TABLE I | ||||||
TDI: LONG-TERM INHALATION STUDY IN RATS | ||||||
Synopsis of tumour incidence (malignant tumours in brackets). | ||||||
Atmospheric concentrations of TDI (ppm) | ||||||
0 | 0.05 | 0.15 | ||||
Sex | ♂ | ♀ | ♂ | ♀ | ♂ | ♀ |
Number of animals examined | 104 | 104 | 104 | 105 | 104 | 105 |
Skin/Adnexa/Glands | ||||||
carcinoma (basal/squamous etc.) | (5) | (3) | (3) | (2) | (6) | 0 |
adenoma | 0 | 0 | 0 | 0 | 3 | 0 |
papilloma | 9 | 1 | 5 | 3 | 3 | 0 |
Mammary gland | ||||||
benign tumour (fibroadenoma etc.) | 4 | 24 | 4 | 27 | 2 | 22 |
multiple benign tumours | 1 | 55 | 0 | 42 | 1 | 52 |
carcinoma + benign tumour | (1) | (9) | 0 | (9) | 0 | (14) |
multiple carcinoma + benign tumour | 0 | (3) | 0 | (1) | 0 | 0 |
mammary tumour (unconf.) | 0 | 1 | 0 | 0 | 0 | 0 |
Subcutis/muscle/bone | ||||||
fibroma | 29 | 1 | 22 | 1 | 35 | 4 |
fibrosarcoma | (1) | (2) | (2) | 0 | (2) | 0 |
lipoma | 10 | 3 | 6 | 0 | 6 | 3 |
osteoma | 0 | 0 | 0 | 0 | 1 | 0 |
osteosarcoma | (1) | 0 | (1) | 0 | (1) | (1) |
lymphangioma | 0 | 0 | 0 | 0 | 1 | 0 |
histiocytoma | (1) | 0 | (4) | 0 | (1) | 0 |
rhabdomyosarcoma | 0 | 0 | (1) | 0 | 0 | 0 |
sarcoma (unclass.) | 0 | 0 | (1) | 0 | 0 | 0 |
Haemopoietic/lymphoreticular | ||||||
malignant lymphoma | (6) | (1) | 0 | (1) | (3) | (3) |
haemangioma | 1 | 1 | 1 | 2 | 4 | 0 |
thymus: thymoma | 0 | (1) | 0 | 1+ (1) | 0 | 1 |
squamous carcinoma | 0 | (1) | 0 | 0 | 0 | 0 |
Uterus | ||||||
polyp | - | 5 | - | 2 | - | 3 |
leiomyoma | 0 | - | 1 | - | 0 | |
sarcoma | - | 0 | - | 0 | - | (1) |
Cervix | ||||||
stromal tumour | - | 2 | - | 2 | - | 0 |
Pancreas | ||||||
islet cell adenoma | 1 | 1 | 2 | 0 | 3 | 2 |
Liver | ||||||
angiosarcoma | 0 | (3) | 0 | (1) | 0 | (3) |
carcinoma | 0 | 0 | (1) | 0 | 0 | (1) |
cholangiocarcinoma | 0 | 0 | (1) | 0 | 0 | 0 |
Jejunum | ||||||
sarcoma | 0 | 0 | (1) | 0 | 0 | 0 |
Stomach | ||||||
adenocarcinoma | 0 | 0 | 0 | (1) | 0 | 0 |
Caecum | ||||||
schwannoma | 0 | 0 | 0 | 0 | 1 | 0 |
leiomyosarcoma | 0 | 0 | 0 | 0 | 0 | (1) |
Rectum | ||||||
polyp | 0 | 0 | 0 | 1 | 0 | 0 |
Lungs | ||||||
adenoma | 2 | 3 | 3 | 0 | 1 | 1 |
Body cavities, membranes, surfaces etc. | ||||||
lipoma | 0 | 1 | 0 | 0 | 0 | 0 |
mesothelioma | 0 | 0 | (1) | 0 | 1 | 0 |
liposarcoma | 0 | 0 | 0 | 0 | (1) | 0 |
haemangioma | 0 | 0 | 0 | 0 | 1 | 0 |
lymphangioma | 0 | 0 | 1 | 0 | 0 | 0 |
Adrenals | ||||||
phaeochromocytoma | 1 | 0 | 1 | 0 | 1 | 0 |
cortical adenoma | 2 | 1 | 1 | 0 | 0 | 1 |
cortical carcinoma | 0 | 0 | 0 | 0 | (1) | 0 |
Pituitary | ||||||
adenoma | 53 | 64 | 32 | 62 | 38 | 67 |
Thyroid | ||||||
c-cell carcinoma | 0 | 0 | 0 | (1) | 0 | 0 |
c-cell adenoma | 11 | 7 | 3 | 1 | 7 | 4 |
follicular adenoma | 1 | 0 | 0 | 0 | 0 | 1 |
Parathyroids | ||||||
adenoma | 0 | 1 | 0 | 0 | 0 | 0 |
Brain | ||||||
meningioma | 0 | 0 | 0 | 0 | 2 | 0 |
astrocytoma | 1 | 0 | 1 | 0 | 0 | 0 |
oligodendroglioma | 1 | 0 | 0 | 0 | 0 | 0 |
Kidneys | ||||||
carcinoma | 0 | 0 | 0 | 0 | 0 | (1) |
liposarcoma | (1) | 0 | (1) | 0 | 0 | 0 |
mesenchymal tumour | 1 | 0 | 0 | 0 | 0 | 0 |
lipomatous tumour | 1 | 0 | 3 | 0 | 0 | 0 |
nephroblastoma | 0 | 0 | 1 | 0 | 0 | 0 |
Testes | ||||||
Leydig cell adenoma | 2 | - | 2 | - | 1 | - |
Epididymides | ||||||
mesothelioma | 0 | - | 1 | - | 0 | - |
Prostate | ||||||
adenocarcinoma | 0 | - | 0 | - | (1) | - |
Ovaries | ||||||
granulosa-theca cell | - | 2 | - | 0 | - | 1 |
Heart | ||||||
angiosarcoma | 0 | (1) | 0 | 0 | 0 | 0 |
Eyes | ||||||
leiomyoma | 0 | 0 | 0 | 1 | 1 | 1 |
Miscellanous | ||||||
squamous cell carcinoma of unknown origin | (1) | 0 | 0 | 0 | 0 | 0 |
Nasal turbinates | No macroscopically diagnosed tissue masses. Histopathology in progress. |
TABLE II | ||||||
TDI: LONG-TERM INHALATION STUDY IN RATS | ||||||
Summary of total tumour incidence | ||||||
Males | Females | |||||
0 ppm | 0.05 ppm | 0.15 ppm | 0 ppm | 0.05 ppm | 0.15 ppm | |
Total animals | 104 | 104 | 104 | 104 | 105 | 105 |
Tumour bearers | 86 | 67 | 81 | 105 | 98 | 101 |
Animals with malignant tumours | 9 | 3 | 10 | 3 | 4 | 5 |
Animals with benign tumours | 69 | 53 | 64 | 84 | 80 | 76 |
Animals with both malignant and benign tumours | 8 | 11 | 7 | 18 | 14 | 20 |
TABLE III | ||||||
MICRONUCLEUS TEST ON RATS EXPOSED TO TDI-VAPOUR FOR 4 WEEKS, PERCENTAGE OF MICRONUCLEATED ERYTHROCYTES, MEANS OF 5 ANIMALS PER SEX PER LEVEL ± STANDARD DEVIATION, 1000 RBC PER ANIMAL EXAMINED | ||||||
Atmospheric concentration of TDI (ppm) | ||||||
0 | 0.05 | 0.15 | ||||
Sex | ♂ | ♀ | ♂ | ♀ | ♂ | ♀ |
Rats | 0.6 ± .9 | 0.5 ± .2 | 0.9 ± .4 | 0.8 ± .l | 0.8 ± .2 | 0.8 ± .4 |
Applicant's summary and conclusion
- Conclusions:
- The study is considered to be reliable (reliability Klimisch 2). The validity criteria of the test system were fulfilled. The test material did induce slight signs of toxicity but no increased incidence of tumours. The test material was considered to be not carcinogenic after exposure via the inhalation route under the conditions of the test. The results of the study did not reveal a substantial carcinogenic potential of TDI, when administered via inhalation to rats.
- Executive summary:
The carcinogenicity of the test material was investigated in rats by Loeser et al (1983). The test was conducted similar to OECD TG451. Groups of male and female rats (21 animals per sex per group) were exposed to 0,05 and 0.15 ppm of toluene-diisocyanate (TDI) by inhalation for 6 h/day, 5 days/week for approx. 2 years. Type and incidence of tumours and the number of tumour-bearing animals were recorded. Additionally clinical signs, mortality, body weight gain, haematology, biochemistry, urinalysis, and cytogenicity were recorded. At termination of the study necropsy and histopathological examination were performed and organ weights recorded. No exposure-related signs occurred during the study. At termination of the study (at week 110 for males and at week 108 for females) total percentage deaths were 65% in controls, 67% low dose, 71% high dose males and 68% in controls, 75% low dose, 64% high dose females. Male and female rats of the 0.15 ppm group gained less weight during the first 12 weeks of the study. Type and incidence of tumours and the number of tumour-bearing animals did not indicate any carcinogenic effect. Haematology, biochemistry, urinalysis, and cytogenicity did not reveal any untoward effect. Histopathological examination in the rat study has not been completed, but no effect in the respiratory tract or in any other tissue has yet been seen.
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