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Diss Factsheets
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EC number: 606-441-0 | CAS number: 201305-16-0
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian germ cell study: cytogenicity / chromosome aberration
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well documented study, conducted similar to guideline.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 974
- Report date:
- 1974
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 478 (Genetic Toxicology: Rodent Dominant Lethal Test)
- Version / remarks:
- (1984)
- Deviations:
- no
- Principles of method if other than guideline:
- The study was conducted before appropriate test guidelines and GLP were introduced.
- GLP compliance:
- no
- Type of assay:
- rodent dominant lethal assay
Test material
- Reference substance name:
- Methyl 4-hydroxybenzoate
- EC Number:
- 202-785-7
- EC Name:
- Methyl 4-hydroxybenzoate
- Cas Number:
- 99-76-3
- IUPAC Name:
- methyl 4-hydroxybenzoate
- Details on test material:
- - Name of test material (as cited in study report): Methylparaben
- Analytical purity: no adta
- Lot/batch No.: 1674K
- Other: used as supplied by the Food and Drug Administration
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: a closed colony (random-bred, not further specified)
- Age at study initiation: 10-12 weeks
- Weight at study initiation: 280 - 350 g (400 g in case of high dose group rats)
- Housing: in groups of 5. Sanitary cages and bedding were used and changed 2 times per week, at which time water containers were cleaned, sanitised and filled. Once a week, cages were repositioned on racks; racks were repositioned within rooms monthly.
- Diet: commercial 4% fat diet, ad libitum until animals were introduced into the experiment
- Water: ad libitum
- Acclimation period: 4-11 days
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: physiol. saline (0.85%)
- Duration of treatment / exposure:
- not applicable
- Frequency of treatment:
- - single exposure: single oral administration
- repeated exposure: once daily on 5 consecutive days, 24 h apart - Post exposure period:
- 8 weeks (sequential matings)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
5, 50, 500, 5000 mg/kg bw
Basis:
actual ingested
- No. of animals per sex per dose:
- 10 males
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Triethylene Melamine, 0.3 mg/kg bw, intraperitoneal injection
Examinations
- Tissues and cell types examined:
- - Determination of fertility index
- Necropsy of the uteri of mated females, analysing early deaths (deciduomata), absorptions, dead implatations, total implantations and number of Corpora lutea - Details of tissue and slide preparation:
- Following treatment, the males were sequentially mated to 2 females per week for 8 weeks (7 weeks in the subacute study). Females were killed 14 days after separating from the males, and at necropsy the uterus was examined for deciduodimata, late foetal deaths and total implantations. Corpora lutea, early fetal deaths, late fetal deaths and total implantations per uterine horn were recorded.
- Evaluation criteria:
- Each male was mated with 2 females per week, and this provided for an adequate number of implantations per group per week (200 minimum) for negative controls, even if there was a 4-fold reduction in fertility of implantations.
- Statistics:
- yes, please refer to "any other information on materials and methods incl. tables".
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- at 1000 mg/kg bw and above
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
Test 1:
- 1000 mg/kg: 1/5 animals dead (Day 3)
- 2000 mg/kg: 2/5 animals dead (Day 2)
- 3000 mg/kg: 4/5 animals dead (Day 1: 3 animals, Day 2: 1 animal)
- 4000 mg/kg: 4/5 animals dead (Day 1: 4 animals)
- 5000 mg/kg: 10/10 animals dead (Day 1: 10 animals)
All animals showed reddened stomach lining and lungs congested. The LD50 value was determined to be 2100 mg/kg bw using the Litchfield-Wilcoxon method.
Test 2:
A single dose of 5000 mg/kg bw was administered to 10 male rats (average body weight: 262 g). No signs of toxicity or abnormal behavior were observed in the 7-day observation period. No deaths occured. At termination all animals were killed and on necropsy no gross findings were observed. The LD50 value was determined to be >5000 mg/kg bw.
RESULTS OF DEFINITIVE STUDY
- 5, 50, 500 mg/kg bw (single exposure):
Significant decreases in average Corpora lutea and preimplantation losses were seen in the experimental groups of Weeks 1, 4 and 5.
- 5, 50, 500 mg/kg bw/day (repeated exposure):
Significant increases in average implantations and Corpora lutea were seen in the experimental groups at week 4. Significant, dose-related increases were seen in average resorptions at 500 mg/kg bw/day at Weeks 1 and 6.
- 5000 mg/kg bw/d (single and repeated exposure):
Treated animals did not significantly vary from those of the vehicle control group, except for a significant increase in the number of dead implants per total of weeks 2 and 6. In these respective examples 1 and 2 were found with 6 or more dead embryos. Omission of these animals from the sample would bring the calculated values into line with those determined for the vehicle controls. Whether these are sporadic phenomena or due to compound effects cannot be determined from the data, although the former is suggested by the lack of effect on the other parameters. The positive control substance Triethylene Melamine caused significant preimplatation loss and embryo resorptions during the first 5 weeks.
Comparing the values obtained by application with 5000 mg/kg bw/day with those of the animals treated with 5, 50, and 500 mg/kg bw/day revealed no dose response or time trend patterns, which would suggest a dominant lethal effect for the test item.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
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