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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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to microorganisms
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with limited documentation / justification
- Justification for type of information:
- Data is from OECD QSAR toolbox version.3.3 and QMRF report has been attached.
- Qualifier:
- according to guideline
- Guideline:
- other: predicted data
- Principles of method if other than guideline:
- Prediction is done using QSAR Toolbox version 3.3 with log kow as the primary discriptors.
- 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:
- not specified
- Test organisms (species):
- Tetrahymena pyriformis
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Key result
- Duration:
- 48 h
- Dose descriptor:
- other: IGC50
- Effect conc.:
- 59.84 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- other: Growth
- Remarks on result:
- other: toxic
- Conclusions:
- Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity on micro-organisms was predicted Bis(4-hydroxy-N-methylanilinium) sulphate (CAS:55-55-0). Growth inhibition concentration i.e IGC50 value was estimated to be 59.84 mg/l for Tetrahymena pyriformis for 48 hrs duration. It was concluded that the Bis(4-hydroxy-N-methylanilinium) sulphate (CAS: 55-55-0) was likely to be toxic to micro-organisms
- Executive summary:
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity on micro-organisms was predicted Bis(4-hydroxy-N-methylanilinium) sulphate (CAS:55-55-0). Growth inhibition concentration i.e IGC50 value was estimated to be 59.84 mg/l for Tetrahymena pyriformis for 48 hrs duration. It was concluded that the Bis(4-hydroxy-N-methylanilinium) sulphate (CAS: 55-55-0) was likely to be toxic to micro-organisms
Reference
The prediction was based on dataset comprised from the following descriptors: IGC50
Estimation method: Takes average value from the 7 nearest neighbours
Domain logical expression:Result: In Domain
((((((((("a" or "b" or "c" or "d" ) and ("e" and ( not "f") ) ) and "g" ) and "h" ) and ("i" and ( not "j") ) ) and ("k" and ( not "l") ) ) and ("m" and ( not "n") ) ) and ("o" and ( not "p") ) ) and ("q" and "r" ) )
Domain logical expression index: "a"
Referential boundary: The target chemical should be classified as Phenols (Acute toxicity) by US-EPA New Chemical Categories
Domain logical expression index: "b"
Referential boundary: The target chemical should be classified as Strong binder, NH2 group AND Very strong binder, OH group by Estrogen Receptor Binding
Domain logical expression index: "c"
Referential boundary: The target chemical should be classified as Strong binder, NH2 group OR Very strong binder, OH group by Estrogen Receptor Binding ONLY
Domain logical expression index: "d"
Referential boundary: The target chemical should be classified as Phenols, Poly by Aquatic toxicity classification by ECOSAR
Domain logical expression index: "e"
Referential boundary: The target chemical should be classified as Not possible to classify according to these rules by DPRA Cysteine peptide depletion
Domain logical expression index: "f"
Referential boundary: The target chemical should be classified as High reactive OR High reactive >> Activated haloarenes OR High reactive >> Aromatic C-Nitroso compounds OR High reactive >> Benzyl halides OR Low reactive OR Low reactive >> N-substituted aromatic amides by DPRA Cysteine peptide depletion
Domain logical expression index: "g"
Referential boundary: The target chemical should be classified as Class 3 (unspecific reactivity) by Acute aquatic toxicity classification by Verhaar (Modified) ONLY
Domain logical expression index: "h"
Referential boundary: The target chemical should be classified as Reactive unspecified by Acute aquatic toxicity MOA by OASIS ONLY
Domain logical expression index: "i"
Referential boundary: The target chemical should be classified as Phenols, Poly by Aquatic toxicity classification by ECOSAR
Domain logical expression index: "j"
Referential boundary: The target chemical should be classified as Anilines (Hindered) OR Anilines (Unhindered) OR Esters OR Hydroquinones OR Phenol Amines OR Phenols by Aquatic toxicity classification by ECOSAR
Domain logical expression index: "k"
Referential boundary: The target chemical should be classified as Aromatic Amine Type Compounds AND Phenol Type Compounds by Oncologic Primary Classification
Domain logical expression index: "l"
Referential boundary: The target chemical should be classified as Halogenated Aromatic Hydrocarbon Type Compounds by Oncologic Primary Classification
Domain logical expression index: "m"
Referential boundary: The target chemical should be classified as H-acceptor-path3-H-acceptor by in vivo mutagenicity (Micronucleus) alerts by ISS
Domain logical expression index: "n"
Referential boundary: The target chemical should be classified as Nitro-aromatic by in vivo mutagenicity (Micronucleus) alerts by ISS
Domain logical expression index: "o"
Referential boundary: The target chemical should be classified as No Data by Ultimate biodeg
Domain logical expression index: "p"
Referential boundary: The target chemical should be classified as > 100 days OR 1 to 10 days by Ultimate biodeg
Domain logical expression index: "q"
Parametric boundary:The target chemical should have a value of log Kow which is >= 0.966
Domain logical expression index: "r"
Parametric boundary:The target chemical should have a value of log Kow which is <= 4.85
Description of key information
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity on micro-organisms was predicted Bis(4-hydroxy-N-methylanilinium) sulphate (CAS:55-55-0). Growth inhibition concentration i.e IGC50 value was estimated to be 59.84 mg/l for Tetrahymena pyriformis for 48 hrs duration. It was concluded that the Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatesilicate (CAS: 63022) was likely to be toxic to micro-organisms
Key value for chemical safety assessment
- EC50 for microorganisms:
- 59.84 mg/L
Additional information
Following studies include the predicted data and experimental study for the target chemical and structurally similar read across to conclude the toxicity extent of 4-aminophenol (CAS: 55-55-0) towards aquatic algae is summarized as follows:
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity on micro-organisms was predicted Bis(4-hydroxy-N-methylanilinium) sulphate (CAS:55-55-0). Growth inhibition concentration i.e IGC50 value was estimated to be 59.84 mg/l for Tetrahymena pyriformis for 48 hrs duration. It was concluded that the Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatesilicate (CAS: 63022) was likely to be toxic to micro-organisms
Further it is supported by the experimental study of structurally similar read across 4-aminophenol (CAS: 123-30-8) from the publication Fresenius Environmental Bulletin 2011,The study was carried out according to the broth macrodilution method to investigate the antibacterial potentials of p-aminophenol. PH of the growth medium had a slight effect on the MIC values and the MIC value was higher in the growth medium with a lower pH. Time-kill analyses of p-aminophenol were performed against Staphylococcus aureus and concn. dependent killing curves were obtained.
The results demonstrated that p-aminophenol could inhibit the bacterial growth.
Minimum inhibitory concentration(MIC) to Staphylococcus aureus is 3.125 mg/L. It can be concluded from the value that the p-aminophenol is toxic to the micro-organisms.
Thus based on the effect concentrations which is in the range 3.125 mg/l to 59.84 mg/l give the conclusion that test substance 4-aminophenol (CAS: 55-55-0) was likely to be toxic to micro-organism at environmentally relevant concentrations and applying weight of evidence approach it can be considered to be toxic as per the CLP classification criteria for aquatic environment.
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