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EC number: 302-639-3 | CAS number: 94114-03-1 A distillation fraction from the hydrogenation of pyrolysis gasoline boiling in the range of approximately 20°C to 200°C (68°F to 392°F).
- 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:
- sub-chronic toxicity: inhalation
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Near guideline, GLP, animal experimental study, available as published report, fully adequate for assessment.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 990
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.29 (Sub-Chronic Inhalation Toxicity:90-Day Study)
- Version / remarks:
- Cited as Directive 87/302/EEC, part B, p. 20
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Toluene
- EC Number:
- 203-625-9
- EC Name:
- Toluene
- Cas Number:
- 108-88-3
- Molecular formula:
- C7H8
- IUPAC Name:
- toluene
- Details on test material:
- Toluene was obtained in one lot (H-12-19-80) from Exxon Company, USA (Baytown, TX, USA) as a clear, colourless liquid. Purity was greater than 99% as determined by elemental analysis, Karl Fischer water analysis and gas chromatography (GC). GC detected three impurities with individual peak areas of less than 0.1% of the major peak area. Benzene content was determined to be 5.7 ppm (v/v). The calculated benzene concentrations were 0.82, 4.1 and 8.2 ppb for the toluene exposures at 120, 600 or 1200 ppm.
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: F344/N
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Portage, MI., USA
- Age at study initiation: approx. 6-7 weeks
- Housing: singly in stainless steel wire mesh cages
- Diet: IH 07 Rat and Mouse Ration (Zeigler Bros., Inc., Gardners, PA) ad libitum (except during exposure)
- Water: ad libitum
- Acclimatisation period: 16 days
ENVIRONMENTAL CONDITIONS
- Temperature: 74-80°F during exposures
- Humidity: 45-55 % during exposures
- Air changes (per hr): not reported
- Photoperiod: 12hrs dark / 12hrs light
IN-LIFE DATES: not reported
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: air
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: no data
- Vapour generation system: toluene vapour was generated by delivering liquid toluene to a heated Spraying Systems atomizer that was operated with nitrogen. Toluene vapour was diluted with chamber ventilation air to produce the desired concentrations in the chamber
- Temperature, humidity: 74-80°F, humidity 45-55 % during exposures
TEST ATMOSPHERE
- Brief description of analytical method used: gas-phase infrared spectrophotometry
- Samples taken from breathing zone: not reported - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- No details reported for 15 week exposure.
- Duration of treatment / exposure:
- 6.5 h/day
- Frequency of treatment:
- 5 days/week for 15 weeks.
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
100, 625, 1250, 2500 and 3000 ppm
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
377, 2355, 4710, 9421 and 11306 mg/m3
Basis:
nominal conc.
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, sham-exposed
- Details on study design:
- Post-exposure period: none
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes (for dead and moribund animals)
- Time schedule: twice/day
DETAILED CLINICAL OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations: beginning of the study and weekly
FOOD CONSUMPTION: No
WATER CONSUMPTION: No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: prior to termination
- Anaesthetic used for blood collection: no data
- Animals fasted: no data
- How many animals: all
- Parameters examined: haemoglobin concentration, haematocrit, total erythrocyte count, platelet count, reticulocyte count and total and differential leukocyte count, mean corpuscular volume, mean corpuscular haemoglobin, mean corpuscular haemoglobin concentration, methaemoglobin concentration
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: prior to termination
- Animals fasted: no data
- How many animals: all
- Parameters examined: blood urea nitrogen (BUN), albumin, albumin/globulin ratio, calcium, chloride, cholinesterase, creatinine, gamma glutamyl transferase, inorganic phosphorus, potassium, glucose, sodium, total bilirubin, total protein
URINALYSIS: No
SPERM MORPHOLOGIC AND VAGINAL CYTOLOGICAL EVALUATIONS: Yes
- Time schedule for evaluation: sperm morphology; at termination (the right cauda epididymis was removed, gently chopped with a scalpel, and incubated for 5 minutes to release its contents) sperm viability and motility were evaluated: vaginal cytology; smears were taken between 7:00 a.m. and 9:00 a.m. from 12-14 consecutive days before the animals were killed and also on the morning of the kill
-
- How many animals: all surviving animals exposed at 0, 100, 625, or 1250 ppm toluene
- Parameters examined: sperm motility - Sacrifice and pathology:
- NECROPSY: Yes
- How many animals: all
ORGAN WEIGHTS: Yes
- brain, liver, lung, right kidney, right testis, and thymus were weighed
HISTOLOGICAL EXAMINATIONS: Yes
- How many animals: all animals that died before the end of the study, vehicle controls, and animals in 2500 and 3000 ppm groups.
- Tissues examined: adrenal glands, aorta, brain, caecum, colon, duodenum, epididymis/prostate/testes or ovaries/uterus, oesophagus, femur, heart, ileum, jejunum, kidneys, liver, lungs and bronchi, mammary gland, mesenteric lymph nodes, nasal tissue, pancreas, parathyroid glands, pituitary gland, preputial gland, rectum, salivary glands, spleen, stomach, thymus, thyroid gland, trachea, and urinary bladder. Sternum examined for the 3000 ppm group and animals dying before the end of the study. Selected tissues of lower dose animals were examined. - Statistics:
- For all end points, dosed groups were compared with the control group using the nonparametric multiple comparison test of Dunn or Shirley. Jonckheere’s test was used to assess the significance of the dose response trends and to determine whether Dunn’s or Shirley’s test was more appropriate for pairwise comparisons.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- effects observed, treatment-related
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- Sperm morphologic and vaginal cytologic evaluations: no effects
Effect levels
open allclose all
- Dose descriptor:
- NOAEC
- Effect level:
- 625 ppm
- Sex:
- male/female
- Basis for effect level:
- other: decrease in leukocyte count in females and relative organ weight increases at 1250 ppm
- Dose descriptor:
- LOAEC
- Effect level:
- 1 250 ppm
- Sex:
- male/female
- Basis for effect level:
- other: decrease in leukocyte count in females, increased relative liver weight in males and increased relative kidney weight in both sexes
- Dose descriptor:
- NOAEC
- Effect level:
- 2 355 mg/m³ air (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: decrease in leukocyte count in females and relative organ weight increases at 4710 mg/m3
- Dose descriptor:
- LOAEC
- Effect level:
- 4 710 mg/m³ air (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: decrease in leukocyte count in females, increased relative liver weight in males and increased relative kidney weight in both sexes
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Haematology and clinical chemistry
Lower leukocyte counts were seen in females at 1250 ppm and above. Plasma cholinesterase activity decreased with increasing exposure concentration.
|
Concentration of toluene (ppm) |
||||||
Parameter |
|
0 |
100 |
625 |
1250 |
2500 |
3000 |
Leukocytes (103/mm3) |
M |
8.19±0.441 |
8.12±0.409 |
7.43±0.367 |
7.19±0.443 |
7.86±0.623 |
7.70±0.095 |
F |
7.26±0.392 |
6.75±0.387 |
6.46±0.480 |
5.98±0.352* |
5.64±0.342** |
6.39±0.385* |
|
Plasma cholinesterase (IU/L) |
M |
714±16 |
712±18 |
682±15 |
671±14 |
630±19 |
595±9** |
F |
3701±83 |
3644±78 |
3166±209* |
297±205 |
1798±162** |
1702±163** |
* P< 0.05, ** P<0.01; M = male, F= females; n=10 for all group except males at 3000ppm, n=2
Organ weights
There were increases in a number of relative organ weights at and above 1250 ppm.
Relative organ weights:
|
Concentration of toluene (ppm) |
||||||
Parameter |
|
0 |
100 |
625 |
1250 |
2500 |
3000 |
Brain |
M |
5.1±0.10 |
5.1±0.10 |
5.2±0.11 |
5.1±0.13 |
5.8±0.11** |
6.7±0.64** |
F |
8.3±0.12 |
8.3±0.12 |
8.2±0.17 |
8.4±0.12 |
9.1±0.14** |
9.1±0.23** |
|
Heart |
M |
2.7±0.04 |
2.8±0.04 |
2.7±0.03 |
2.7±0.04 |
3.0±0.05** |
3.1±0.02** |
F |
3.1±0.04 |
3.1±0.04 |
3.1±0.05 |
3.0±0.07 |
3.3±0.07** |
3.4±0.05** |
|
Kidney |
M |
3.3±0.04 |
3.4±0.05 |
3.3±0.07 |
3.4±0.05* |
3.8±0.07** |
4.0±0.06** |
F |
3.4±0.06 |
3.4±0.07 |
3.4±0.07 |
3.6±0.05* |
3.8±0.05** |
3.8±0.05** |
|
Liver |
M |
35.8±0.58 |
36.0±0.61 |
37.6±0.55 |
38.9±0.54** |
41.0±0.60 |
47.6±0.79 |
F |
34.1±0.55 |
34.8±0.85 |
33.8±0.33 |
34.6±0.46 |
39.5±0.54** |
41.1±0.54** |
|
Lung |
M |
3.3±0.06 |
3.4±0.05 |
3.4±0.05 |
3.5±0.08 |
3.8±0.07** |
3.9±0.16** |
F |
4.5±0.07 |
4.6±0.07 |
4.5±0.08 |
4.7±0.08 |
4.9±0.10** |
4.9±0.08** |
* P< 0.05, ** P<0.01; M = male, F= females
Applicant's summary and conclusion
- Conclusions:
- Toluene exposure at concentrations ≥ 1250 ppm, 6h/day, 5 days per week for 15 weeks induced adverse clinical signs, lower bodyweight and changes in haematology and organ weights.
- Executive summary:
The sub-chronic toxicity of toluene was evaluated in a 15 week inhalation study in rats. Groups of 10 male and 10 female F344/N rats were exposed via inhalation t0 0, 100, 625, 1,250, 2,500, or 3,000 ppm (0, 377, 2,355, 4,710, 9,421, or 11,306 mg/m3) toluene 6.5 hours/day for 5 days/week for 15 weeks. The rats were observed for clinical signs daily, and weighed once per week, blood was collected prior to termination for haematological and clinical chemistry investigations. All animals were necropsied, organs weighed and tissues at 0, 2,500 and 3,000 ppm and from all decedents were examined microscopically.
Eight male rats of the 3000 ppm group died during week 2. The mean body weights of rats exposed to 2500 or 3000 ppm were 15-25% lower than that of controls. Clinical signs included dyspnea in all exposed groups, except males exposed at 3000 ppm and females exposed at 1250 ppm, and ataxia in rats exposed at 3000 or 2500 ppm. The relative kidney weight was statistically significantly increased at 1250 ppm and higher in both sexes. Males at 1250 ppm and higher also showed a statistically significantly increased relative liver weight while females at 2500 ppm and higher showed this effect. Relative weight of the brain, heart, and lung were statistically significantly increased in both sexes at 2500 and 3000 ppm. In male rats, relative testes weight was statistically significantly increased at 2500 and 3000 ppm. Plasma cholinesterase activity decreased as exposure concentration increased, and the leukocyte count was decreased for female rats at 1250 ppm or higher. No compound-related effects were seen on sperm or on oestrous cycle.
A NOAEC of 625 ppm toluene (2,355 mg/m3) can be derived on the basis of a lower leukocyte count in females and increased relative liver and kidney weights at 1250 ppm and above.
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