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EC number: 202-307-7 | CAS number: 94-13-3
- 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
Endocrine disrupter mammalian screening – in vivo (level 3)
Administrative data
- Endpoint:
- endocrine disrupter mammalian screening – in vivo
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 009
Materials and methods
Test material
- Specific details on test material used for the study:
- 17a-ethinylestradiol (EE), propyl p-hydroxybenzoate (propylparaben),
fulvestrant known as ICI 182,780 or Faslodex (Howell et al., 2002;
Tang et al., 2008), and corn oil were obtained from Sigma-Aldrich, Inc. (St Louis,
MO). Butyl
p-hydroxybenzoate (butylparaben) was purchased from Sigma-Aldrich GmbH
(Steinheim, UK). Isopropyl p-hydroxybenzoate (isopropylparaben) and isobutyl
p-hydroxybenzoate (isobutylparaben) were obtained from Tokyo Kasei Kogyo
Co. Ltd (Tokyo, Japan). All stock chemicals were dissolved in ethanol.
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on species / strain selection:
- Sprague-Dawley immature female rats were purchased from SamTaKo-Bio Korea (Chungbuk, Korea)
- Sex:
- female
- State:
- immature female
- Details on test animals and environmental conditions:
- The rats were
housed in polycarbonate cages in a controlled environment (temperature,
23C ± 2C; relative humidity, 50 ± 10%; frequent ventilation; and an
illumination schedule of 12-h light/12-h dark). The experimental animals
were given free access to food and tap water. Rats were fed a diet of soyfree
pellets with a standard laboratory diet (Samyang formula feed;
Samyang Oil & Feed Co., Ltd, Seoul, Republic of Korea). The component
phytoestrogen-free AIN-76A-purified diet was used in order to rule out
potential estrogenic effects of phytoestrogens (Mitchell et al., 1989). All
experimental procedures were approved by the Ethics Committee of
Chungbuk National University.
Administration / exposure
- Route of administration:
- oral: gavage
- Details on oral exposure:
- From postnatal days (PND) 14 to 16, immature female rats (n= 8 per each group, mean body weight [BW]: 27.47± 0.69 g) received a sc injection daily of the following: propyl-, isopropyl-,butyl-, or isobutylparaben at a dose of 62.5, 250, or 1000 mg/kg BW/day;17a-ethinylestradiol (1 mg/kg BW/day) as a positive control; or corn oil (5 ml/kg BW/day) as a negative control. Dosages were adjusted according to changes in BW. BWs, clinical signs, and abnormal behaviors were recorded daily throughout the experimental period. In the second experiment, rats were administered fulvestrant (1 mg/kg BW/day) 30 min before chemical treatments. All animals were euthanized by ethyl ether 24 h after the final treatment. The uteri were weighed and prepared for samples of total RNAs and proteins. Each exposure was performed in triplicates.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 62.5 mg/kg bw/day (nominal)
- Remarks:
- propyl-, isopropyl-, butyl-, and isobutylparaben
- Dose / conc.:
- 250 mg/kg bw/day (nominal)
- Remarks:
- propyl-, isopropyl-, butyl-, and isobutylparaben
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- Remarks:
- propyl-, isopropyl-, butyl-, and isobutylparaben
Examinations
- Statistics:
- Data were analyzed by one-way ANOVA, followed
by Tukey’s test for multiple comparisons of columns. Statistical analysis was
performed using GraphPad Prism4 for Windows Edition (GraphPad Software
Inc., La Jolla, CA). A p value of < 0.05 was considered statistically significant.
Results and discussion
Results of examinations
- Details on results:
- Uterotrophic Effects Induced by Parabens:
The uterotrophic assay is a standard reliable method used to detect the estrogenicity of environmental compounds in vivo (Diel et al., 2000; Kang et al., 2000; Newbold et al., 2001; Padilla-Banks et al., 2001). Female rats at PND 14 were treated with increasing doses (62.5, 250, and 1000 mg/kg BW) of parabens (propyl-, isopropyl-, butyl-, and isobutylparaben) for 3 days. The highest dosage of isopropyl-, butyl-, and isobutylparaben significantly increased uterine wet weight. EE treatment, used as a positive control, induced a significantly increased uterine weight (fourfold vs. vehicle, p <
0.05). However, no significant effect was detected in the propylparaben-treated groups.
Effects of Parabens on CaBP-9k mRNA and Protein Expression:
The effects of parabens on the uterine CaBP-9k mRNA level and protein expression were examined using an immature rat model. CaBP-9k transcripts were induced by the highest dose of isopropyl-, butyl-, and isobutylparaben (13.6-, 12.4-, and 6.9- fold increases vs. vehicle, respectively). The positive
control, EE, induced uterine CaBP-9k transcription (p < 0.05). However, all concentrations of propylparaben and the middle and lowest concentration of the other parabens did not affect CaBP-9k gene expression.Similar to that observed for mRNA expression, uterine CaBP-9k protein levels were upregulated by EE and parabens, with the exception of propylparaben.
Applicant's summary and conclusion
- Executive summary:
no significant effects on uterine weight were detected for any dose of propylparaben.
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