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EC number: 202-448-4 | CAS number: 95-76-1
- 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:
- short-term repeated dose toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Original report not yet available, cited in EU risk assessment
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- A 2-week subchronic inhalation study on 3,4-dichloroaniline in rats
- Author:
- Kinney, LA et al.
- Year:
- 1 987
- Bibliographic source:
- the toxicologist 7(1): 192
- Reference Type:
- other: study report; no access
- Title:
- Unnamed
- Year:
- 1 986
- Reference Type:
- secondary source
- Title:
- 3,4-dichloroaniline (3,4-DCA)
- Author:
- EU-Risk Assessment Report
- Year:
- 2 006
- Bibliographic source:
- EUR 22235 EN; ISSN 1018-5593
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EU Method B.8 (Subacute Inhalation Toxicity: 28-Day Study)
- Deviations:
- yes
- Remarks:
- ; 14 days
- GLP compliance:
- not specified
Test material
- Reference substance name:
- 3,4-dichloroaniline
- EC Number:
- 202-448-4
- EC Name:
- 3,4-dichloroaniline
- Cas Number:
- 95-76-1
- Molecular formula:
- C6H5Cl2N
- IUPAC Name:
- 3,4-dichloroaniline
- Details on test material:
- - Name of test material (as cited in study report): 3,4-dichloroaniline
- Analytical purity: no data
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: CRl:CD_BR
- Sex:
- male
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- nose/head only
- Vehicle:
- other: unchanged (no vehicle)
- Remarks on MMAD:
- MMAD / GSD: vapour
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 6 h/d
- Frequency of treatment:
- 5 d/week
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
10 mg/m³
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
45 mg/m³
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
200 mg/m³
Basis:
nominal conc.
- No. of animals per sex per dose:
- 20 male per dose
- Control animals:
- yes, concurrent no treatment
Results and discussion
Results of examinations
- Clinical signs:
- not specified
- Mortality:
- not specified
- Body weight and weight changes:
- not specified
- 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:
- effects observed, treatment-related
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- not specified
- Histopathological findings: neoplastic:
- not specified
- Details on results:
- see remarks on results
Effect levels
- Dose descriptor:
- LOAEC
- Effect level:
- 10 mg/m³ air (nominal)
- Sex:
- male
- Basis for effect level:
- other: overall effects
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
3,4-dichloroaniline caused dose-dependent methemoglobinemia in all exposed rats (2.5-, 5.0- and 40 -fold increases over control values, respectively) No biological changes in response to the methemoglobinemia were observed at 10 mg/m³. At 45 and 200 mg/m³, rats had accumulations of hemosiderin in the spleen. at 200 mg/m³, rats had elevated spleen weights and extramedullary hematopoeisis in the spleen. These rats also had depressed erythrocyte count, hemoglobin concentration and hematocrit and elevated platelet count and mean corpuscular volume.
These changes are suggestive of increased erythrocyte destruction at 45 and 200 mg/m³, with a resultant compound-related anemia and enhanced erythropoeisis at 200 mg/m³.
Applicant's summary and conclusion
- Executive summary:
Kinney, LA (1986)
Test atmospheres containing both vapour and solid particles of 0, 10, 45 or 200 mg/m³ of 3,4-dichloroaniline (99.35% purity) were exposed for 2 weeks (nose-only, 6 hours/day, 5 days/week) to male Crl:CD BR rats (Kinney, 1986). From a total of 20 rats per group 10 rats were used to determine toxic effects, 5 of which were killed after 10th exposure and 5 rats per group were allowed to recover for 14 days post-exposure. Testing parameters included urinalysis after the 9th exposure, haematology and clinical chemistry examinations on day 10 of treatment and on day 14 of recovery, weighing of 6 organs and histopathological examinations of 28 organs/tissues. The remaining 10 rats per groups were used to monitor methaemoglobin level alternately on each second day for half of each group. For these rats no other data are reported due to the potentially confounding effects of repeated bleeding. Time points of methaemoglobin analyses immediately after blood sampling are of critical value (Beutler et al., 1995), but were not reported in this study. At the end of treatment, 3,4-dichloroaniline caused dose-dependent methaemoglobinemia in all exposed rats, dose-related increased incidences of minimal accumulation of hemosiderin in the spleen of mid and high dose rats (5/5 rats at high dose, 2/4 rats at mid dose), anemia, significantly elevated spleen weights (absolute and spleen/body weight) and mild extramedullary haematopoiesis in high dose rats. Anemia was characterised by significantly depressed erythrocyte counts (-17% at 200 mg/m³), reduced concentrations of haemoglobin and hematocrit, elevated platelet count and elevated mean corpuscular volume (MCV), MCH, and MCHC after the 10th exposure. Mean methaemoglobin levels were 12.2% (minimum-maximum 10.0-18.4%, except values on treatment-free weekend) in the high and 1.6% (minimum - maximum 1.0-2.1%) in the mid dose group. In the low dose group a significantly raised methaemoglobin level of 0.8% (minimum - maximum 0.7-1.1%) was found. Although these values are within the range of normal values, they are corresponding to an approximately 2.5-fold increase above control (mean methaemoglobin value 0.3%, minimum - maximum. 0.2-0.5%). No other treatment-related changes were found in the 10 mg/m3 group at the end of the treatment period. No significant clinical signs or body weight changes were observed in rats exposed to 10 or 45 mg/m³ of 3,4-dichloroaniline. Rats exposed to 200 mg/m³ had significantly depressed body weights compared to controls after the 1st and 6th exposures; body weights for these rats were generally lower than controls throughout the exposure period. Various non-specific clinical signs (low incidences of dry red nasal and ocular discharges, brown discoloured fur, stained perineum, hair loss) were observed during the exposure period (mainly in the 1st treatment week). During the recovery period, the body weight of rats exposed to 200 mg/m³ remained (non-significantly) lower than that of other groups. Hemosiderosis was still found in mid and high dose animals after 14 days of recovery being more pronounced and more frequent than after the 10th exposure. All rats were affected; the severity was mild in high dose rats and minimal in mid dose animals. Some blood cell parameters (depressed erythrocyte counts (-9.5%), increased MCV) were still changed at 200 mg/m³. The number of erythrocytes were significantly lower in the low and mid dose group (-7.2% and ¿7.4%) than those of the control groups after recovery. Methaemoglobin level of the low dose rats returned to the range of control animals three days after the end of exposure, while methaemoglobin levels in mid and high dose groups remained significantly elevated through the recovery period. No adverse effect was seen in the lungs, trachea and nose examined histopathologically. In this study, the NOAEC for systemic effects was not derived; the NOAEC for local effects on the respiratory tract was 200 mg/m³. With respect to systemic toxic effects at the end of treatment, the concentration of 3,4-dichloroaniline effective to induce hemosiderosis and methaemoglobin concentrations above the normal range was 45 mg/m³. However this concentration is not considered to be the LOAEC, because the erythrocyte counts in the low and mid dose decreased during recovery. Although their values represented only mild anemia, they were significantly below those of control groups after recovery time. The significant increase of methaemoglobin levels at the low dose group in comparison to the control values, the return of increased methaemoglobin levels after the third day of recovery and the delayed effect on erythrocytes during recovery support that 10 mg/m³ represents the LOAEC.
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