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EC number: 274-581-6 | CAS number: 70356-09-1
- 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
Specific investigations: other studies
Administrative data
Link to relevant study record(s)
- Endpoint:
- endocrine system modulation
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Well conducted study meeting generally accepted scientific principles, acceptable for assessment.
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- In this study, six extensively used ultraviolet (UV) filters were assessed for transcriptional activation of estrogen receptors using a sensitive in vitro reporter gene assay.
Briefly, Human embryonal kidney 293 (HEK293) cells were stable transfected with hERalpha and hERbeta. The compounds to be tested were added to the cells and incubated for 24h before luciferase reading. Furthermore, an in vivo assay was used for which zebrafish, in which an estrogen responsive luciferase reporter gene has been stably introduced, were incubated for 96h before they were sacrificed and luciferase activity was read from homogenised fish samples. - GLP compliance:
- no
- Type of method:
- other: in vitro and in vivo
- Species:
- other: human embryonal kidney cells (HEK 293) and zebrafish
- Strain:
- not specified
- Sex:
- not specified
- Route of administration:
- oral: drinking water
- Vehicle:
- ethanol
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- In vitro assay: 24 h
In vivo assay: 96 h - Frequency of treatment:
- one application
- Post exposure period:
- not applicable
- Dose / conc.:
- 0.1 other: µmol/L
- Remarks:
- in vitro assay
Basis: nominal in water - Dose / conc.:
- 1 other: µmol/L
- Remarks:
- in vitro assay
Basis: nominal in water - Dose / conc.:
- 10 other: µmol/L
- Remarks:
- in vitro assay
Basis: nominal in water - Dose / conc.:
- 100 other: µmol/L
- Remarks:
- in vitro assay
Basis: nominal in water - Dose / conc.:
- 10 other: µmol/L
- Remarks:
- in vivo assay
Basis: nominal in water - No. of animals per sex per dose:
- In vitro assay: no data on cell density was given
In vivo assay: 5 - 6 fish were exposed per concentration - Control animals:
- yes, concurrent vehicle
- Details on results:
- IN VITRO ASSAY
The test substance butyl methoxydibenzoylmethane (BMDBM) was able to significantly induce the human estrogen receptor alpha (hERalpha) in stably transfected HEK293 cells at concentrations of 10 and 100 µmol/L up to approximately 40 % of maximal 17beta-estradiol induction. Induction of human estrogen receptor beta (hERbeta) was only achievable with the highest tested concentration of 100 µmol/L (significant induction to 10 - 15 % of maximal 17beta-estradiol induction).
The anti-estrogenic potential was assessed using a competition assay with a sub-maximal concentration of estradiol. BMDBM showed no dose-dependent anti-estrogenic effect at either hERalpha or hERbeta. Whereas at best a slight reducing effect was observable for hERalpha, either tested concentration of BMDBM reduced hERbeta transcription to about 60 % of maximal estradiol induction.
IN VIVO ASSAY
Neither BMDBM at 10 µmol/L nor one of the other tested UV filters tested could not induce transcriptional activation of the estrogen receptor in zebrafish. The positive control (17beta-estradiol, 10 nmol/L) showed a clear response. - Conclusions:
- The observed slight induction of human estrogen receptor-alpha by BMDBM (10 - 100 µM) in the in vitro assay could not be confirmed in the in vivo zebrafish assay.
- Executive summary:
In this study, six extensively used ultraviolet (UV) filters were assessed for transcriptional activation of estrogen receptors using an in vitro reporter gene assay and an in vivo zebrafish luciferase assay.
IN VITRO ASSAY
The test substance butyl methoxydibenzoylmethane (BMDBM) was able to significantly induce the human estrogen receptor alpha (hERalpha) in stably transfected HEK293 cells at concentrations of 10 and 100 µmol/L up to approximately 40 % of maximal 17beta-estradiol induction. Induction of human estrogen receptor beta (hERbeta) was only achievable with the highest tested concentration of 100 µmol/L (significant induction to 10 – 15 % of maximal 17beta-estradiol induction).
The anti-estrogenic potential was assessed using a competition assay with a sub-maximal concentration of estradiol. BMDBM showed no dose-dependent anti-estrogenic effect at either hERalpha or hERbeta. Whereas at best a slight reducing effect was observable for hERalpha, either tested concentration of BMDBM reduced hERbeta transcription to about 60 % of maximal estradiol induction.
IN VIVO ASSAY
Neither BMDBM at 10 µmol/L nor one of the other tested UV filters tested could induce any transcriptional activation of the estrogen receptor in zebrafish. The positive control (17beta-estradiol, 10 nmol/L) showed a clear response.
The observed slight induction of human estrogen receptor-alpha by BMDBM (10-100 µM) in the in vitro assay could not be confirmed in the in vivo zebrafish assay.
- Endpoint:
- endocrine system modulation
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Well conducted study, meets generally acepted scientific principles, acceptable for assessment.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The interaction of five polycyclic musk compounds and seven UV filters with the estrogen receptor (ER), androgen receptor (All), and progesterone (PR) receptor were assessed, using sensitive and specific reporter gene cell lines, namely stably transfected HEK293 cells (for ERa and ERb) and the AR- and PR-CALUX® bioassays.
- GLP compliance:
- no
- Type of method:
- in vitro
- Species:
- other: stably transfected HEK293 (human embryonic kidney cells), stably transfected U2-OS (human osteosarcoma) cells (for the CALUX® assays)
- Strain:
- not specified
- Sex:
- not specified
- Route of administration:
- other: incubation in medium
- Vehicle:
- ethanol
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 24h incubation period
- Frequency of treatment:
- once
- Post exposure period:
- no
- Remarks:
- Doses / Concentrations: 0.1 - 10 µM (AR repression assay)
Basis: nominal conc. - Remarks:
- Doses / Concentrations: 1 nM - 10 µM (PR repression assay)
Basis: nominal conc. - No. of animals per sex per dose:
- Three independent experiments with each concentration measured in triplicate.
- Details on results:
- All UV filters were reported to show agonism toward hERa, and additionally, a number were found to show agonism toward hERb as well (Schreurs et al. 2000). None of the UV filters showed anti-estrogenic effects.
None of the test compounds showed AR transactivation, however, nearly all test compounds were found to be AR antagonists. BMDBM showed no distinct hAR transcription repression inside the chosen concentration range. Extrapolation outside the tested dose range resulted in an IC50 value of 11 µM.
None of the test compounds showed PR transactivation (data not shown); however, several test compounds, but not BMDBM, were found to be PR antagonists. - Conclusions:
- Butyl methoxydibenzoylmethane (BMDBM) showed weak ERa agonism and weak androgen receptor antagonism in in vitro reporter gene assays. No influence on progesteron receptor was observed.
- Executive summary:
The interaction of five polycyclic musk compounds and seven UV filters with the estrogen receptor (ER), androgen receptor (All), and progesterone (PR) receptor were assessed, using sensitive and specific reporter gene cell lines, namely stably transfected HEK293 cells (for ERa and ERb) and the AR- and PR-CALUX® bioassays.
In short, all UV filters were reported to show agonism toward hERa, and additionally, a number were found to show agonism toward hERb as well (Schreurs et al. 2000). None of the UV filters showed anti-estrogenic effects.
None of the test compounds showed AR transactivation, however, nearly all test compounds were found to be AR antagonists. BMDBM showed no distinct hAR transcription repression inside the chosen concentration range. Extrapolation outside the tested dose range resulted in an IC50 value of 11 µM.
None of the test showed PR transactivation (data not shown); however, several test compounds, but not BMDBM, were found to be PR antagonists.
Taken together, butyl methoxydibenzoylmethane (BMDBM) only showed weak ERa agonism and weak AR antagonism.
Referenceopen allclose all
Description of key information
Schreurs 2002: The observed slight induction of human estrogen receptor-alpha by BMDBM (10-100 µM) in the in vitro assay could not be confirmed in the in vivo zebrafish assay.
Schreurs 2005: Butyl methoxydibenzoylmethane (BMDBM) showed weak ERa agonism and weak androgen receptor antagonism in in vitro reporter gene assays. These effects were observed by nearly all tested compounds. No influence on the progesterone receptor was observed.
Additional information
Two studies were found that report on endocrine activity of butyl methoxydibenzoylmethane (BMDBM). Two publications of Schreurs et al. (2002 and 2005) stated that slight induction of human estrogen receptor-alpha by BMDBM was observed in vitro. But as all tested substances showed a similar induction of the estrogene receptor which could not be reproduced in an in vivo zebrafish assay, and none of the other publications support this finding, the observed induction of the estrogen receptor remains questionable.
Based on these results it was concluded that BMDBM possesses no endocrine activity.
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