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EC number: 202-977-0 | CAS number: 101-80-4
- 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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- long-term toxicity to fish, other
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Not specified.
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- US EPA standardised method used. GLP not specified. Results taken from TSCA fiche OTS0546071.
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- other: EPA method 1000.0 (3rd ed.; EPA/600/4-91/002)
- Deviations:
- no
- Principles of method if other than guideline:
- Chronic Toxicity
The procedure used in the test followed EPA method 1000.0 (3rd ed.; EPA/600/4-91/002). The test had a total of 4 replicates of 10 organisms per concentration (0, 2.5, 5, 10, 20, and 40 mg/L). Cadmium chloride was tested as a reference toxicant. The test was performed using the target temperature of 25+1°C and a 16-hour light/8-hour dark photoperiod. Synthetic moderately hard water served as laboratory dilution water for the test. The water was stored at 20°C under gentle aeration until needed, up to 14 days. Stocks of the test substance were prepared each day in moderately hard synthetic freshwater, and these stocks were used to dose the test solutions. Larval fish <24 hours old were randomly loaded into test chambers. During testing, fish were fed a suspension of brine shrimp daily. The test solutions were renewed daily.
Mortality observations were recorded daily. Temperature, pH, dissolved oxygen, and conductivity were measured in the new and old test solutions daily, and at test termination. Growth of the larvae were measured at the termination of the test.
The results of the toxicity tests were analyzed using the ToxCalc statistical software package and followed US EPA guidance. - GLP compliance:
- no
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material:
- Analytical monitoring:
- no
- Details on sampling:
- - Concentrations: A rangefinding toxicity tests used the concentration series of 100, 50, 25, 12.5 and 6.25 mg/L oxydianiline and a dilution water control. The definitive toxicity test used the concentration series of 40, 20, 10, 5 and 2.5 mg/L oxydianiline and a dilution water control.
- Sampling method: None
- Sample storage conditions before analysis: The test solutions were renewed each day by siphoning 80 percent of the old test solutions from the test vessels and replacing with freshly made test solutions, made at the time. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Stocks of the test substance were prepared each day in moderately hard synthetic freshwater, and these stocks were used to dose the test solutions.
- Eluate: Synthetic moderately hard water (US EPA 1993) served as laboratory dilution water for the tests. Batches of this water were made by passing deionized water through activated carbon, adding reagent grade chemicals, and aerating overnight. The water was stored at 20°C under gentle aeration until needed up to, 14-days.
- Controls: Cadmium Chloride
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): Not applicable
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)): Not applicable
- Evidence of undissolved material (e.g. precipitate, surface film, etc): Not specified
- Conductivity: 254 - 384 µS/cm - Test organisms (species):
- Pimephales promelas
- Details on test organisms:
- Pimephales promelas (fathead minnow) were obtained from EA's Culture Facility. Brood organisms were maintained in recirculating dechlorinated tap water at 20°C in 10-gallon aquaria. For the chronic toxicity tests, eggs produced from the brood system were removed from the brood aquaria and placed into dechlorinated tap water at 25°C for the incubation period. Newly hatched larvae, less than 24 hours old, from lots FH 2-9/25-26 were used in the chronic definitive toxicity testing..
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 7 d
- Post exposure observation period:
- None
- Hardness:
- Not measured
- Test temperature:
- Chronic Definitive: 24.0-25.7 (°C)
- pH:
- Chronic Definitive: 7.4-8.4
- Dissolved oxygen:
- Chronic Definitive: 6.0-8.1 mg/L
- Salinity:
- Not applicable.
- Nominal and measured concentrations:
- Chronic definitive toxicity test: 40, 20, 10, 5 and 2.5 mg/L test substance and a dilution water control.
- Details on test conditions:
- For the P. promelas chronic toxicity tests, larval fish <24 hours old were randomly loaded into the test chambers. The rangefinding test had a total of 2 replicates of 10 organisms per concentration and control. The definitive test had a total of 4 replicates of 10 organisms per concentration and control. The test chambers were 1-liter plastic beakers with 250 ml of test solution. During testing, organisms in each test chamber were fed daily a suspension of brine shrimp Artemia nauplii. The uneaten and dead brine shrimp were removed from the test vessels daily. The test solutions were renewed each day by siphoning 80 percent of the old test solutions from the test vessels and replacing with freshly made test solutions.
- Reference substance (positive control):
- yes
- Remarks:
- Cadmium chloride
- Key result
- Duration:
- 7 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 7 d
- Dose descriptor:
- LOEC
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 7 d
- Dose descriptor:
- other: IC25
- Effect conc.:
- 14.1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: (confidence limits, 12.0-31.2 mg/L)
- Details on results:
- Results of the definitive P. promelas definitive test were similar to the range fnding (see results of the acute toxicity test). At test termination, there was 15 percent survival in 40 mg/L test substance concentration and 55 percent survival in the 20 mg/L test substance concentration. Both concentrations were sigificantly different (p=0.05) from the control which had 98 percent survival. There was a minimum of 84 percent survival in the 2.5 to 10 mg/L test substance concentrations. Mean growth in the 10 mg/L test substance concentration (0.524 mg/organism) was significantly different (p = 0.05) from the control which had 0.659 mg/organism. Mean growth in the 2.5 mg/L and 5 mg/L test substance concentrations was 0.606 and 0.627 mg/organism, respectively. Using growth as the most sensitive test endpoint, the NOEC was 5 mg/L test substance , the LOEC was 10 mg/L test substance. The IC25 was 14.1 mg/L test substance .
- Results with reference substance (positive control):
- Results with cadmium chloride: IC25= 22.1 mg/l CdCl2 ; acceptable control chart limits of 11.2 - 35.2 mg/l.
- Reported statistics and error estimates:
- The results of the toxicity tests were analyzed using the ToxCalc statistical software package (Version 5.0, Tidepool Scientific Software) and followed US EPA guidance (US EPA 1994).
- Validity criteria fulfilled:
- yes
- Remarks:
- The result with the reference substance, cadmium chloride is within the range of acceptability
- Conclusions:
- 3,4'-oxydianiline is of moderate concern for chronic toxicity to fish after 7 days of expsure (NOEC = 5 mg/L). The lowest concentration at which a toxicity was observed was 10 mg/L (16% mortality and a significant effect on growth)
- Executive summary:
A chronic toxicity test was conducted on Pimephales promelas larvae for 7 days according to US EPA standard. The test was perfomed under semi-static conditions with a renewal of the test concentrations by 80% every day. All validity criteria are fulfilled and the results are expressed as nominal concentrations. As the substance does not degrade rapidly in water, those nominal concentrations are considered to be representative of actual concentrations. The results of the tests lead to a NOEC of 5 mg/L (based on growth of larvae). This result can be used in the dossier and for classification of 4,4'-oxydianiline.
Reference
Results of the chronic definitive test with fish larvae
Nominal test concentration (mg/L) | 96h - % survival | 7d % survival | Mean growth (mg/organism +/- SD) |
Control | 98 | 98 | 0.659 +/- 0.098 |
2.5 | 98 | 98 | 0.606 +/- 0.052 |
5.0 | 98 | 98 | 0.627 +/- 0.027 |
10 | 84 | 84 | 0.524 +/- 0.063* (p<0.05) |
20 | 60 | 55 | 0.453 +/- 0.076 |
40 | 18 | 15 | 0.155 +/- 0.139 |
96h LC50 = 22.7 mg/L (18.7 - 27.5 mg/L) 95%IC
NOEC = 5 mg/L
LOEC = 10 mg/L
Description of key information
A chronic toxicity test on the analogue 3,4'-oxydianilline was conducted on Pimephales promelas larvae for 7 days according to US EPA standard. The test was perfomed under semi-static conditions with a renewal of the test concentrations by 80% every day. The results of the tests lead to a NOEC of 5 mg/L (based on growth of larvae).
This result can be used in the dossier and for classification of 4,4'-oxydianiline.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 5 mg/L
Additional information
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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