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EC number: 202-811-7 | CAS number: 100-02-7
- 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
Endpoint summary
Administrative data
Description of key information
Key value for chemical safety assessment
Additional information
According to regulation (EC) 1907/2006 of the European parliament and the council of 18 December 2006 (Article 18),
repeated dose toxicity on transported isolated intermediates needs to be described, if data on this endpoint are available,
but no chemical safety assessment is necessary. Therefore, publicly available data on repeated dose toxicity of 4 -Nitrophenol
is summarized in the following, but no key values were defined for 4 -Nitrophenol.
In the Concise International Chemical Assessment Document (CICAD) as well as in the BUA report, information on repeated dose toxicity of PNF is reviewed. CICAD: In a 13-week gavage study, Sprague-Dawley rats (20 per sex per dose group) were given 0, 25, 70, or 140 mg 4-nitrophenol/kg bwin water 5 days/week. Premature deaths were seen in animals dosed at 70 and 140 mg/kg bw (1 male and 1 female at 70 mg/kg bwand 15 males and 6 females at 140 mg/kg bw); these were usually preceded by clinical signs, including pale appearance, languid behaviour, prostration, wheezing, and dyspnoea, shortly after dosing. The histopathological examination of these animals revealed minimal to moderately severe congestion in the lung, liver, kidney, adrenal cortex, and pituitary; in surviving animals, no treatment-related changes compared to controls were report ed. Only a provisional NO(A)EL based on changes in liver, kidneys, and lungs of 25 mg/kg bw can be derived from this study (Hazleton Lab., 1989).Dermal application of 4-nitrophenol to Swiss-Webster mice (10 per sex and dose group; given 0, 22, 44, 88, 175, or 350 mg/kg bw in acetone, 3 times per week over 13 weeks) resulted in dose-dependent mortality as well as skin irritation/inflammation and necrosis at > 175 mg/kg bw (cited from NTP). In a long-term study with Swiss-Webster mice (50 per sex per dose group), 4-nitrophenol in acetone was applied to the interscapular skin at doses of 0, 40, 80, or 160 mg/kg body weight, 3 days/week for 78 weeks. At termination of the study, the survival rates were 29/60, 17/60, 26/60 and 24/60 for males and 35/60, 26/60, 33/60 and 27/60 for females. The increased mortality after 60 weeks was due to a generalized amyloidosis (the severity of the amyloidosis was similar among dosed and control animals) and secondary kidney failure. The final mean body weights of the dosed animals were similar to those of the controls. NTP (1993) stated that there were no substance-related neoplastic or non-neoplastic effects associated with the dermal administration of 4-nitrophenol and that there was no evidence of a carcinogenic activity of the substance in male or female mice. BUA report: Administration of 0, 62.5, 125, 250, 500 or 1000 mg/kg bw/d of 4 -nitrophenol in corn oil to CD-1 mice over a period of 8 days by gavage resulted in an LD50 value of 626 mg/kg bw with a 95% confidence interval of 456 -895 mg/kg bw (Plasterer et al, 1985).In a 28 -day subchronic toxicity test according to OECD guidelines, male and female Sprague-Dawley rats (10/dose group) were administered daily dosages of 70, 210 or 630 mg 4 -nitrophenol/kg/d by gavage (Andrae et al, 1981). According to the report of Leuschner, 1980, motoric inhibition, which lasted for up to 2 hours, was seen in the animals of the two highest dosage groups immediately after administration. One male of the middle dose group and 4 males and 6 females of the highest dose group died. In the lowest dose group, pale liver and fatty degenreation of liver were observed; the latter of which was also seen at 210 mg, but due to the early mortality not at the highest dose group. All of the animals which died prematurely, showed vascular congestion. In addition, nephrosis, testicular athrophy, inhibition of spermatogenesis and follicular atresia in the ovaries were seen. No NOEL can be derived from the study, as at the lowest dosage group tested, effects of treatment were observed. It is pointed out, that the dosage levels chosen were at leasdt in part in the range of acute toxicity.
Justification for classification or non-classification
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