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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2017-08-21 to 2018-09-26
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 211 (Daphnia magna Reproduction Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.20 (Daphnia magna Reproduction Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling method: duplicate samples were taken from the test medium with the nominal test item concentration of 6.0 μg/L and from the solvent control at the start of the test (Day 0) and at nine further sampling dates distributed over the test period. The analytical samples were taken from the different replicates of each treatment.
For verification of the test item concentration in the application solution, duplicate samples were taken at the start and the end of all application solution renewal periods.
- Sample storage conditions before analysis: To each 10-mL test medium sample, a volume of 10 mL of acetonitrile was added immediately after sampling. Then, the samples were stored frozen (at about –20 °C) until analysis. In preexperiments for investigation of the storage stability of the test medium samples, the test item proved to be stable under these storage conditions. - Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Chemical name of vehicle: N,N-Dimethylformamide (DMF)
- Concentration of vehicle in test medium: Refer to section "Any other information on materials and methods incl. tables" - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Strain/clone: Straus
- Age at study initiation: less than 24 hours old
- Method of breeding: under identical conditions to the test conditions
- Source: in-house culture (origin: Daphnia Collection of the University of Basel/Switzerland)
- Age of parental stock: at least 14 days old
- Feeding during test : yes
- Food type: suspension of green algae of the species Desmodesmus subspicatus
- Amount: 0.3 mg C/L at the start of the test, As the parental daphnids were growing during the test, the concentration was adjusted to 0.4 mg C/L at Day 7 and to 0.5 mg C/L at Day 14. Automatically dosed in volumes of 200 μL to each aliquot of test
water.
- Frequency: daily
ACCLIMATION
- Acclimation period: No acclimation needed, an in-house culture bred under identical conditions to those of the tests were used for this study. - Test type:
- flow-through
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 21 d
- Hardness:
- 2.5 mmol/L (= 250 mg/L as CaCO3)
- Test temperature:
- 20 °C
- pH:
- 7.8 - 8.1
- Dissolved oxygen:
- 9.0 - 9.7 mg/L
- Nominal and measured concentrations:
- Nominal concentration: 6 µg/L
Mean measured concentration: 3 µg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: flow-through glass beaker
- Material, size, headspace, fill volume: 50 mL fill volume
- Type of flow-through: computer-controlled automated flow-through dosing system
- Renewal rate of test solution (frequency/flow rate): Flow rate - approximately 19-fold test medium exchange rate per day
The application solution was renewed three times during the test period (Days 4, 11 and 18).
- No. of organisms per vessel: 1
- No. of vessels per concentration (replicates): 20
- No. of vessels per control (replicates): 10
- No. of vessels per vehicle control (replicates): 20
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Elendt M7 Medium, prepared according to OECD 211
- Alkalinity: 0.9 mmol/L
- Culture medium different from test medium: no, the same
OTHER TEST CONDITIONS
- Adjustment of pH: none
- Photoperiod: 16 h light : 8 h dark
- Light intensity: approximately 3 μE m-2 s-1.
EFFECT PARAMETERS MEASURED:
- daily for immobility of adults or other visible abnormalities
- body length at the end of the test on the surviving adults
- reproduction rate at the end of the test
TEST CONCENTRATIONS
- Results used to determine the conditions for the definitive study: Based on a series of a stirring and rande-finding experiments, it was determined that the test item has a very low solubility in the test media and the test concentration could not be maintained stable during the exposure period without using a solubilising agent. Thus, the solvent DMF was use to achieve a relatively stable test concentration in the flow-through system. - Reference substance (positive control):
- no
- Key result
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 3 µg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Remarks on result:
- other: nominal: 6 µg/L
- Duration:
- 21 d
- Dose descriptor:
- LOEC
- Effect conc.:
- > 3 µg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Remarks on result:
- other: nominal: 6 µg/L
- Key result
- Duration:
- 21 d
- Dose descriptor:
- EC10
- Effect conc.:
- > 3 µg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Remarks on result:
- other: nominal: 6 µg/L
- Details on results:
- The 21-day EC10 values for the mortality, inhibition of the reproduction rate and body length could not be calculated, since no inhibitory effect of the test item on daphnia at the test concentration of nominal 6.0 μg/L was observed.
- Validity criteria fulfilled:
- yes
- Conclusions:
- In conclusion, the test item Butyl methoxydibenzoyl methane had no toxic effects on survival, growth and reproduction of Daphnia magna after the exposure period of 21 days at the mean measured concentration of 3.0 μg/L, corresponding to the highest concentration of test item that could be reached in test water. Thus, the 21-day NOEC of the test item was determined to be 3.0 μg/L (mean measured), representing the water solubility limit of the test item. The 21-day LOEC and the 21-day EC10 values for the different endpoints were > 3.0 μg/L.
- Executive summary:
The impact of the test item Butyl methoxydibenzoyl methane on the survival, growth (body length) and reproduction rate of Daphnia magna was investigated in a flow-through test over 21 days following the OECD 211 and the Commission Regulation (EC) No 440/2008, C.20 (amended by Commission Regulation (EC) No. 2017/735).
In this flow-through test, 10 single-housed daphnids were exposed to untreated test water (control) and 20 single-housed daphnids each were exposed to untreated test water with solvent (solvent control) or to treated test water (test medium) with a test item concentration of nominal 6.0 μg/L. This test item concentration was chosen to maintain a constant exposure concentration at the solubility limit of the test item in test water, i.e. approximately 2 μg/L, as determined in a pre-experiment.
A limit test was performed to demonstrate that the test item Butyl methoxydibenzoyl methane has no toxic effects on Daphnia magna at the highest concentration of the test item that could be reached in test water. The concentrations of the test item Butyl methoxydibenzoyl methane measured in the test medium with the nominal test concentration of 6.0 μg/L were between 40 and 66 % of the nominal value during the test period. The mean measured concentration during the test period was 3.0 μg/L ± 0.47 μg/L (arithmetic mean ± standard deviation), corresponding to 50 % of the nominal value. The losses are attributed to intrinsic properties of the difficult test item with low water solubility. All reported biological results are related to the mean measured concentration of 3.0 μg/L.
All parental daphnids in the control, the solvent control and test item treatment group survived until the end of the test. The first brood was recorded at the same time in both controls and the treatment group. The mean reproduction rate and the mean body length for the test item treatment were not significantly different than the control and the solvent control.
In conclusion, the test item Butyl methoxydibenzoyl methane had no toxic effects on survival, growth and reproduction of Daphnia magna after the exposure period of 21 days at the mean measured concentration of 3.0 μg/L corresponding to the highest concentration of the test item that could be reached in test water.
Thus, the 21-day NOEC of the test item was determined to be 3.0 μg/L (mean measured) representing the water solubility limit of the test item. The 21-day LOEC and the 21-day EC10 values for the different endpoints were > 3.0 μg/L.
Reference
Analytical Results
The measured test item concentration in the freshly prepared application solutions (DMF/water) was between 83 and 95 % of the nominal value. In the aged application solutions, the test item concentration was between 81 and 91 % of nominal. Thus, the stability of the test item in the application solution during its use for 7 days could be demonstrated.
The concentrations of the test item Butyl methoxydibenzoyl methane measured in the test medium with the nominal test concentration of 6.0 μg/L were between 40 and 66 % of the nominal value. The mean measured concentration during the exposure period was calculated as arithmetic mean over all measurements and was 3.0 μg/L ± 0.47 μg/L, corresponding to 50 % of the nominal value. This recovery is in the range of what was expected according to dosing pre-experiments. The losses could be attributed to intrinsic properties of the difficult test item with low water solubility. The measured concentration of 3.0 μg/L corresponded to the solubility limit of the test item in test water of approximately 2 μg/L. All reported biological results are related to the mean measured concentration of 3.0 μg/L.
The method of analysis was validated and proven to be suitable for use. The mean measured test item concentration per sampling ranged from 2.40 to 3.98 μg/L during the test period.
Biological Results
In the control, the solvent control and the mean measured test item concentration of 3.0 μg/L, all parental daphnids survived until the end of the test. Therefore, the NOEC for mortality was determined to be 3.0 μg/L, corresponding to the solubility limit of the test item in the test water.
The first offspring released from their parent daphnids were recorded in both the controls and at the mean measured test item concentration of 3.0 μg/L on Day 8. Thus, the time of the first brood was not affected by the test item. The mean reproduction rate of the daphnids in the control and solvent control was 158 ± 22 (mean ± standard deviation) and 151 ± 22 living offspring per surviving adult, respectively. At the mean measured test item concentration of 3.0 μg/L the mean reproduction rate was 157 ± 26, corresponding to 104 % of the solvent control value. Therefore, the NOEC for inhibition of reproduction rate was determined to be 3.0 μg/L (solubility limit).
The mean body length of the daphnids in the control and solvent control was 4.9 ± 0.10 mm (mean ± standard deviation) and 4.8 ± 0.14 mm, respectively. At the mean measured test item concentration of 3.0 μg/L the mean body length was 4.9 ± 0.10 mm, corresponding to 101 % of the solvent control value. Therefore, the NOEC for body length was determined to be 3.0 μg/L L (solubility limit).
The 21-day EC10 value for mortality, inhibition of the reproduction rate and body length could not be calculated, since no toxic effects of the test item on daphnia at the mean measured test concentration of 3.0 μg/L were observed. No visible abnormalities were observed in the test animals during the test.
Table 1: Biological endpoints
Biological Endpoints |
Nominal Test Item Concentration |
||
Control |
Solvent |
6.0 µg/L |
|
Survival [%] after |
100 |
100 |
100 |
Mean Reproduction Rate |
158 |
151 |
157 |
Mean Reproduction Rate in % of Solvent Control |
104 |
- |
104 |
Mean Body Length of the Adults [mm] |
4.86 |
4.84 |
4.88 |
Mean Body Length in % of Solvent Control |
100 |
- |
101 |
Description of key information
The test item Butyl methoxydibenzoyl methane had no toxic effects on survival, growth and reproduction of Daphnia magna after the exposure period of 21 days at the mean measured concentration of 3.0 μg/L, corresponding to the highest concentration of test item that could be reached in test water. Thus, the 21-day NOEC of the test item was determined to be 3.0 μg/L (mean measured), representing the water solubility limit of the test item. The 21-day LOEC and the 21-day EC10 values for the different endpoints were > 3.0 μg/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 3 µg/L
Additional information
The impact of the test item Butyl methoxydibenzoyl methane on the survival, growth (body length) and reproduction rate of Daphnia magna was investigated in a flow-through test over 21 days following the OECD 211 and the Commission Regulation (EC) No 440/2008, C.20 (amended by Commission Regulation (EC) No. 2017/735).
In this flow-through test, 10 single-housed daphnids were exposed to untreated test water (control) and 20 single-housed daphnids each were exposed to untreated test water with solvent (solvent control) or to treated test water (test medium) with a test item concentration of nominal 6.0 μg/L. This test item concentration was chosen to maintain a constant exposure concentration at the solubility limit of the test item in test water, i.e. approximately 2 μg/L, as determined in a pre-experiment.
A limit test was performed to demonstrate that the test item Butyl methoxydibenzoyl methane has no toxic effects on Daphnia magna at the highest concentration of the test item that could be reached in test water. The concentrations of the test item Butyl methoxydibenzoyl methane measured in the test medium with the nominal test concentration of 6.0 μg/L were between 40 and 66 % of the nominal value during the test period. The mean measured concentration during the test period was 3.0 μg/L ± 0.47 μg/L (arithmetic mean ± standard deviation), corresponding to 50 % of the nominal value. The losses are attributed to intrinsic properties of the difficult test item with low water solubility. All reported biological results are related to the mean measured concentration of 3.0 μg/L.
All parental daphnids in the control, the solvent control and test item treatment group survived until the end of the test. The first brood was recorded at the same time in both controls and the treatment group. The mean reproduction rate and the mean body length for the test item treatment were not significantly different than the control and the solvent control.
In conclusion, the test item Butyl methoxydibenzoyl methane had no toxic effects on survival, growth and reproduction of Daphnia magna after the exposure period of 21 days at the mean measured concentration of 3.0 μg/L corresponding to the highest concentration of the test item that could be reached in test water.
Thus, the 21-day NOEC of the test item was determined to be 3.0 μg/L (mean measured) representing the water solubility limit of the test item. The 21-day LOEC and the 21-day EC10 values for the different endpoints were > 3.0 μg/L.
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.