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EC number: 200-237-1 | CAS number: 55-55-0
- 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

Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- secondary literature
- Justification for type of information:
- Data is from secondary literature.
- Qualifier:
- according to guideline
- Guideline:
- other: As mentioned below
- Principles of method if other than guideline:
- Pimephales promelas Bioassay was carried out under static to study the effects of Bis(4-hydroxy-N-methylanilinium) sulphate on aquatic environment.
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material: p-Methylaminophenol sulfate- IUPAC name: Bis(4-hydroxy-N-methylanilinium) sulphate- Molecular formula: C14H20N2O6S- Molecular weight: 344.386 g/mole- Smiles:CNc1ccc(cc1)O.CNc1ccc(cc1)O.OS(=O)(=O)O- Inchl: 1S/2C7H9NO.H2O4S/c2*1-8-6-2-4-7(9)5-3-6;1-5(2,3)4/h2*2-5,8-9H,1H3;(H2,1,2,3,4)- Substance type: Organic- Physical state: Solid crystalline (off white - white)
- Analytical monitoring:
- not specified
- Vehicle:
- yes
- Remarks:
- distilled water
- Details on test solutions:
- - Stock solutions: Stock solutions of the chemicals to be tested were prepared with distilled water. Appropriate volumes of these solutions were dispensed into the test containers, mixed with the diluent water.- Control : concurrent
- Test organisms (species):
- Pimephales promelas
- Details on test organisms:
- TEST ORGANISM- Common name: Fathead Minnow- Source: Muskie Hatchery, Asbury, New Jersey- Feeding during test: daily Feeding was suspended 2 days prior to each experiment.ACCLIMATION- Acclimation period: 2 weeks or longer- Acclimation conditions (same as test or not): same as test
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Test temperature:
- 54.5 (37.0 -75.0) F
- pH:
- 7.0-7.5
- Dissolved oxygen:
- >=4 mg/l
- Details on test conditions:
- TEST SYSTEM- Test vessel: five 50-gallon glass aquaria- No. of organisms per vessel: 4 individuals/gallon- Aeration: 48-hour diffused aerationEach acclimation tank was equipped with three Metaframe Model118 "Bubble up" filter aerators. Each aerator consisted of achamber containing activated charcoal and cotton. A sourceof oil-free compressed air was supplied to each unit. Inaddition to providing continuous aeration and recirculation ofwater, these filter-aerators also served as a substrate forbiological growths, needed for the decomposition of fish wasteproducts.OTHER TEST CONDITIONSApplication frequency: 1X
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.25 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- coagulation of the embryo
- Remarks on result:
- other: toxic
- Sublethal observations / clinical signs:
Bioassay data summary of Pimephales promelas
Cumulative mortalities
Percent
mortality at
Test chemical
Conc. (mg/l)
Starting population
24 hr
48
hr
72
hr
96
hr
96 hrs
96hr LC50
or range (mg/l)
4-methylAmino
Phenol Sulfate
(IIIP2)
0.25
15
8
0
0
0
53.3
0.25
0.14
15
0
0
0
0
0.0
0.08
15
0
0
0
0
0.0
0.045
15
0
0
0
0
0.0
0.025
15
0
0
0
0
0.0
0.0
15
0
0
0
0
0.0
- Conclusions:
- The lethal concentration LC50 to 50 % of Pimephales promelas is 0.25 mg/l at 96 hrs. Mortality was observed during the assay. It can be concluded from the value that the Bis(4-hydroxy-N-methylanilinium) sulphate is toxic to the aquatic fish.
- Executive summary:
A Pimephales promelas bioassay examined under static condition to study the effects of Bis(4-hydroxy-N-methylanilinium) sulphate at concentration range of 0.0, 0.025, 0.045, 0.08, 0.14, 0.25 mg/L.
Each bioassay series was conducted over the recommended 96 hour period. Moribund fish were removed from the test containers, and their numbers recorded on a daily basis. Daily monitoring for pH and dissolved oxygen was practiced. A minimum dissolved oxygen concentration of 4 mg/l was presumed acceptable for a valid experiment, and at no time during the program did the dissolved oxygen fall below this level.Similarly, no significant pH changes were observed. At least one control unit was included with every experiment. It contained the same number of fish as an individual test unit and served as a monitor of the diluent water. At highest concentration level, 53.3% mortality was observed in 96 hrs.
The lethal concentration LC50 to 50 % of Pimephales promelas is 0.25 mg/l. Hence from the value it can be concluded that the Bis(4-hydroxy-N-methylanilinium) sulphate is toxic to the aquatic fish and can be considered as “aquatic acute 1” as per classification for aquatic environment.
Reference
Description of key information
A Pimephales promelas bioassay examined under static condition to study the effects of Bis(4-hydroxy-N-methylanilinium) sulphate at concentration range of 0.0, 0.025, 0.045, 0.08, 0.14, 0.25 mg/L.
Each bioassay series was conducted over the recommended 96 hour period. Moribund fish were removed from the test containers, and their numbers recorded on a daily basis. Daily monitoring for pH and dissolved oxygen was practiced. A minimum dissolved oxygen concentration of 4 mg/l was presumed acceptable for a valid experiment, and at no time during the program did the dissolved oxygen fall below this level.Similarly, no significant pH changes were observed. At least one control unit was included with every experiment. It contained the same number of fish as an individual test unit and served as a monitor of the diluent water. At highest concentration level, 53.3% mortality was observed in 96 hrs.
The lethal concentration LC50 to 50 % of Pimephales promelas is 0.25 mg/l. Hence from the value it can be concluded that the Bis(4-hydroxy-N-methylanilinium) sulphate is toxic to the aquatic fish and can be considered as “aquatic acute 1” as per classification for aquatic environment.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 0.25 mg/L
Additional information
Following studies includes the experimental study for the target chemical and structurally similar read across to conclude the toxicity extent of 4-aminophenol (CAS: 55-55-0) towards fishe is summarized as follows:
The exoerimental study of the target chemical from Environmental Effect of Photoprocessing Chemicals Vol I and II 1974, suggests that, A Pimephales promelas bioassay examined under static condition to study the effects of Bis(4-hydroxy-N-methylanilinium) sulphate at concentration range of 0.0, 0.025, 0.045, 0.08, 0.14, 0.25 mg/L.
Each bioassay series was conducted over the recommended 96 hour period. Moribund fish were removed from the test containers, and their numbers recorded on a daily basis. Daily monitoring for pH and dissolved oxygen was practiced. A minimum dissolved oxygen concentration of 4 mg/l was presumed acceptable for a valid experiment, and at no time during the program did the dissolved oxygen fall below this level.Similarly, no significant pH changes were observed. At least one control unit was included with every experiment. It contained the same number of fish as an individual test unit and served as a monitor of the diluent water. At highest concentration level, 53.3% mortality was observed in 96 hrs.
The lethal concentration LC50 to 50 % of Pimephales promelas is 0.25 mg/l. Hence from the value it can be concluded that the Bis(4-hydroxy-N-methylanilinium) sulphate is toxic to the aquatic fish and can be considered as “aquatic acute 1” as per classification for aquatic environment.
Above study is supported by the another experimental study of target chemical from Environmental Protection Agency 1992, which also suggegsts that the Short-term toxicity to fish was carried out under static to study the effects of Bis(4-hydroxy-N-methylanilinium) sulphate on aquatic environment.
The lethal concentration LC50 to 50 % of Fathead minnows is 0.3 mg/l at 96 hrs. Mortality was observed during the assay. It can be concluded from the value that the Bis(4-hydroxy-N-methylanilinium) sulphate is toxic to the aquatic fish. Hence from the value it can be concluded that the Bis(4-hydroxy-N-methylanilinium) sulphate is toxic to the aquatic fish and can be considered as “aquatic acute 1” as per classification for aquatic environment.
Further the assissted by the structurally similar read across 4-aminophenol (CAS: 123-30-8) from J-Check 2010, inidctaes that the Short-term toxicity to fish test was carried out according to the OECD Guideline 203 (Fish, Acute Toxicity Test) at concentrations of2.00, 1.33, 0.889, 0.593, 0.395 mg/L to study the effects of 4-aminophenol on fish.
Test was carried out underflow-throughcondition at 24±1 degree C in 1.8 L per vessel, using 10 organismsper concentration. Aeration was not provided, Photoperiod: room light, 16 hours light - 8 hours dark. Mortalitywas observed during the test.
The lethal concentration LC50 to 50% ofOryzias latipesin 96 hr is 0.925 mg/L. It can be concluded from the value that the 4-aminophenol is toxic to the fish and can be considered as “Aquatic Acute 1” as per the classification for aquatic environment.
Thus based on the effect concentrations which is in the range 0.25 mg/l to 0.925 mg/l give the conclusion that test substance 4-aminophenol (CAS: 55-55-0) was likely to be toxic to fish at environmentally relevant concentrations and applying weight of evidence approach it can be considered to be“Aquatic Acute 1”as per the CLP classification criteria for aquatic environment.
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