Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 200-533-0 | CAS number: 62-44-2
- 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
Supporting study: A repeated dose toxicity study of 4 weeks in rats was conducted on the test item and LOEL observed was 500 mg/kg bw/day, based on haematological findings.
Supporting study: A repeated dose toxicity study of 66 weeks in rats was conducted on the test item and MTD observed was 450 mg/kg bw/day. Based on a significant decrease of renal concentrating capacity and this impairment tended to be rapidly reversible after discontinuation administration of the test item.
Key value for chemical safety assessment
- Toxic effect type:
- dose-dependent
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 1967
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Principles of method if other than guideline:
- The test perfomrs rat experiments with long-term feeding with phenacetin to measure the renal concentration capacity, to find out whether and induced decrease in the renal concentrating capacity would be normalized after discontinuing the drug and to examine the kidney morphology.
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Anticimex AB, Stockholm
- Weight at study initiation: 190g
- Fasting period before study: no
- Diet: ad libitum.
- Water: tap water ad libitum - Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- Group 1: receiving powdered food
Group 2: Rats receiving the powdered food to which phenacetin was added in an amount of 5.35 g/kg food (16 rats).
Group 3: Rats receiving the powdered food, to which acetylsalicylic acid was added, in an amount of 2.70 g/kg food (16 rats). - Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 66 weeks. The rats had free access to food and tap water. After 40 weeks on this regimen 11 rats in group I, 12 in group II, and 13 in group III were killed and autopsied. In the remaining rats the test was continued for 3 more weeks. The drugs were then discontinued. After 23 additional weeks with control food for all three groups, the remaining 12 rats were killed and autopsied.
- Frequency of treatment:
- daily
- Dose / conc.:
- 0 mg/kg diet
- Dose / conc.:
- 5 350 mg/kg diet
- Dose / conc.:
- 2 700 mg/kg diet
- No. of animals per sex per dose:
- Group 1: controls; powdered food with no test item (16 rats)
Group 2: powdered food with phenacetin in an amount of 5.35 g/kg food (16 rats)
Group 3: powdered food with in an amount of 2.70 g/kg food (16 rats) - Control animals:
- yes, plain diet
- Observations and examinations performed and frequency:
- BODY WEIGHT: Yes
- Time schedule for examinations: 2,4,6,8,10,12,14,16,18,20,22,24,26,28,30,32,34,36,38 weeks
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes
URINALYSIS: Yes
- Time schedule for collection of urine: various times after withdrawal of the drugs (1,3,7,12,18 weeks)
- Metabolism cages used for collection of urine:No
- Animals fasted: No
- Parameters checked in table [1], Maximale urine osmolality mOsm/kg H2O, were examined. - Clinical signs:
- not examined
- Mortality:
- not examined
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- There was no definite difference in weight gain between the rats in the three groups.
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- The food intake was greatest for the phenacetin group,
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Endocrine findings:
- not examined
- Urinalysis findings:
- effects observed, treatment-related
- Description (incidence and severity):
- After 38 weeks, there was a significantly lowered osmolality in both the phenacetin group. After 41 weeks there was a significantly lower osmolality in both the phenacetin group. The effect is reversible, therefore an MTD= 450 mg/kg is stablished.
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Gross pathological findings:
- not examined
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Key result
- Dose descriptor:
- other: MTD (maximum tolerated dose)
- Effect level:
- 450 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- urinalysis
- Key result
- Critical effects observed:
- no
- Conclusions:
- In a repeated dose toxicity test of 66 weeks, the MTD (maximum tolerated dose) of the test item in Sprague-Dawley rats was 450 mg/kg bw/d.
- Executive summary:
A 66 weeks repeated dose toxicity study was conducted with the test item. Female rats of Sprague-Dawley strain were used for this study. Control group recieved powdered food with no test item and rats receiving test item was in amount of 5.35 g/kg food. There was a significant decrease of renal concentrating capacity and this impairment tended to be rapidly reversible after discontinuation of the administration of the test item. Therefore, the MTD (maximum tolerated dose) was 450 mg/kg bw/d.
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 1983
- Reliability:
- 2 (reliable with restrictions)
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- In this paper it is reviewed the methods available fot the detection of hemolytic properties of chemicals.
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: SIV 50, Ivanovas, Kissleg, F.R.G.
- Weight at study initiation: 180- 200 g
- Housing: Macrolon cages with wood shavings as bedding under controlled conditions of humidity, temperature and light.
- Water: ad libitum.
- Food: ad libitum rat chow. - Route of administration:
- oral: gavage
- Details on oral exposure:
- ADMINISTRATION:
Phenacetin (Ph. Eur., Merck, Darmstadt, F.R.G.) was administered by stomach tube to 5 rats in a dose of 500 mg/kg, 5 times weekly, as a suspension in 0.5 % methyl cellulose in a volume of 2 ml/kg. - Duration of treatment / exposure:
- 28 days
- Frequency of treatment:
- 5 times weekly
- Dose / conc.:
- 500 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- - 5 males were given: in a dose of 500 mg/kg, 5 times weekly, as a suspension in 0.5 %
methyl cellulose in a volume of 2 ml/kg.
- 5 males (controls): received the vehicle only
- 10 males were given: phenacetin or 0.5 % methyl cellulose (same treatment as above) for osmotic fragility and surface area/volume ratio tests. - Control animals:
- yes, concurrent vehicle
- Details on study design:
Twenty rats were randomly divided into three treatment groups and a control group, and each group had 5 rats being all males. Phenacetin (Ph. Eur., Merck, Darmstadt, F.R.G.) was administered by stomach tube to 5 rats in a dose of 500 mg/kg, 5 times weekly, as a suspension in 0.5 % methyl cellulose in a volume of 2 ml/kg. Controls received the vehicle only (n = 5). Drug treatment was discontinued after 4 weeks. In a separate experiment, two groups of 5 rats were given phenacetin or 0.5 % methyl cellulose (same treatment as above) for osmotic fragility and surface area/volume ratio tests.- Observations and examinations performed and frequency:
- HEMATOLOGIC PARAMETERS:
- Time: at 2 and 4 weeks of phenacetin treatment and 2 weeks after discontinuation of the drug.
- RBC count, Hkt ratio, and MCV were measured with a Coulter Counter, Model S.
- The number of Ret and Heinz body formation were determined in freshly prepared blood smears.
- MHb was assayed spectrophotometrically as the difference in absorbance of cyan-MHb with and without previous addition of ferricyanide.
OSMOTIC FRAGILITY AND SURFACE/VOLUME RATIO OF ERYTHROCYTE:
- Osmotic fragility tests as described by Beutler for human RBC were adapted for rat RBC. 1.5 ml blood was drawn percutaneously into a heparinized 5-ml syringe from the V. subclavia in light ether anesthesia.
- For estimating the surface/volume ratio of RBC, the maximal volume of globular red cell ghosts was determined. - Clinical signs:
- effects observed, non-treatment-related
- Mortality:
- no mortality observed
- Body weight and weight changes:
- not examined
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Test item caused reversible formation of methemoglobin and Heinz bodies and an increase in peripheral reticulocytes after 2 and 4 weeks of treatment. Furthermore, an increase in the mean corpuscular volume of red blood cells (RBC) and the volume of RBC ghosts in hypotonic solutions, and a decrease of the mean corpuscular fragility was observed. The latter changes are considered to be a consequence of regenerative RBC compensation rather than due to structural membrane alteration caused by the test item.
The results suggest that only a combination of several hematological tests can provide comprehensive information about the hemolytic potential of chemical substances, and that for screening purposes small numbers of animals are often sufficient. - Clinical biochemistry findings:
- effects observed, non-treatment-related
- Endocrine findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- effects observed, non-treatment-related
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- not examined
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- not examined
- Dose descriptor:
- LOEL
- Effect level:
- 500 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- haematology
- Critical effects observed:
- no
- Conclusions:
- In a 4-week study and that the LOEL is based on haematological effects. The low observed effect level (LOEL) of the test item in rats was 500 mg/kg bw/day
- Executive summary:
A repeated dose toxicity study in rats was conducted with the test item. The administration of the test item was by oral gavage and the dose used was of 500 mg/kg. Also, a control group was monitored. Haematological and clinical-chemistry examinations were performed and haematological effects on MHb and Heinz bodies were observed. Therefore, the low observed effect level (LOEL) of the test item in rats was 500 mg/kg bw/day.
Referenceopen allclose all
Table 1. Kidney function and phenacetin
Group | No. of rats | Maximale urine osmolality mOsm/kg H2O (mean and standard error of mean) | ||||||
Period of drug consumption (weeks) | Various times after withdrawal of the drugs (weeks) | |||||||
38 | 41 | 1 | 3 | 7 | 12 | 18 | ||
I | 4 | 2592±220 | 2872±76 | 2752±152 | 2942±101 | 3133±408 | 2592±156 | 2750±153 |
II | 5 | 2398±81 | 2264±125 | 2466±201 | 2901±231 | 2442±236 | 2354±184 | 2786±193 |
III | 3 | 2027±102 | 2170±112 | 2624±116 | 2396±112 | 2564±104 | 2249±88 | 2478±72 |
Table 1: METHEMOGLOBIN (MHb), RETICIJLOCYTE RATIO (Ret), HEINZ BODY RATIO (Heinz), RED
BLOOD CELL (RBC) COUNT, AND HEMATOCRIT (Hkt) OF FRESHLY OBTAINED ERYTHROCYTES
Duration of treatment | MHb (%) | Ret (per 10^3 RBC) | Heinz (per 10^3 RBC) | RBC (10^12/1) | Hkt |
2 weeks | |||||
Phenacetin | 7.2±7.9^a | 156±19^a | 118±16^a | 5.930.09^a | 0.40±0.004^a |
Controls | 1.2±0.4 | 28±3 | 0 | 7.74±0.16 | 0.47±0.009 |
4 weeks | |||||
Phenacetin | 12.0±0.8^a | 41±4^a | 7±3^a | 7.09±0.12^a | 0.44±0.009 |
Controls | 7.6±1.7 | 29±3 | 0 | 7.55±0.13 | 0.42±0.004 |
2 weeks after drug | |||||
Phenacetin | 2.7±0.3 | 29±1 | 0 | 7.19±0.16 | 0.40±0.009 |
Controls | 2.9±0.2 | 24±1 | 0 | 7.66±0.12 | 0.40±0.004 |
Table 2: MEAN CORPUSCULAR VOLUME (MCV) OF RED BLOOD CELLS (RBC) IN ISOTONIC PBS,
AND VOLUME AND SURFACE AREA OF RBC GHOSTS IN HYPOTONIC (0.3%) PBS
Duration of treatment | MCV ( μm^3) | Volume (V) of RBC ghosts ( μm^3) | Surface area (S) of RBC ghosts ( μm^2) | S/V ratio |
2 weeks | ||||
Phenacetin | 68±0.7^a | 124±1.8 | 120±1.2 | 0.968 |
Controls | 60±0.2 | 122±1.8 | 119±1.1 | 0.975 |
4 weeks | ||||
Phenacetin | 62±0.4^a | 134±2.2^a | 127±1.4^a | 0.945^a |
Controls | 55±0.3 | 118±1.6 | 116±1.1 | 0.986 |
2 weeks after drug continuation | ||||
Phenacetin | 56±0,2^a | nd | nd | nd |
Controls | 53±0.4 |
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Justification for classification or non-classification
Based on the available data, for repeated dose toxicity, the substance is not classified
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.