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EC number: 427-440-1 | CAS number: 24487-91-0
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 19 February 1997 - 21 February 1997
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted to GLP in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 997
- Report date:
- 1997
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- -
- EC Number:
- 427-440-1
- EC Name:
- -
- Cas Number:
- 24487-91-0
- Molecular formula:
- C9H9ClO2
- IUPAC Name:
- 2-Methyl-3-methoxy benzoyl chloride
- Test material form:
- other: solid
- Details on test material:
- MMBC
Appearance: Light brown solid
Storage conditions: In darkness at room temperature
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
The test substance rapidly hydrolysed to MMBA.
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- Nominal test concentrations: 4.58, 9.96, 21.9, 45.8 and 99.6 mg test substance equivalents/L.
Mean measured test concentrations: 4.90, 10.7, 23.2, 46.6 and 100 mg test substance equivalents/L.
Test concentrations were verified by chemical analysis. 10 mL samples were taken from the pooled replicates of control and each test concentration at 0 hours and after 48 hours.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- DILUTION WATER
The test organisms were maintained and the tests conducted in a reconstituted medium Elendt M4. The medium was prepared using analytical grade reagents and reverse purified deionised water.
Elendt M4 medium
-Trace elements mg/L
H3BO3 2.85
MnCI2.4H2O 0.36
LiCl 0.31
RbCI 0.071
SrC12.6H2O 0.152
NaBr 0.016
Na2MoO4.2H2O 0.063
CuCl.2H2O 0.0165
ZnCl2 0.013
CoCI2.6H2O 0.010
KI 0.0033
Na2. SeO3 0.0022
NH4VO3 0.00058
Fe-EDTA solution 3.54
-Macro nutrients mg/L
CaCl2.2H2O 294
MgSO4.7H2O 123
KCl 5.80
NaHCO3 64.8
Na2.SiO3.5H2O 6.83
NaNO3 0.274
KH2PO4 0.143
K2HPO4 0.184
-Vitamins mg/L
Thiamine hydrochloride 0.075
Cyanocobalamine (B 12) 0.0010
Biotine 0.00075
TEST SUBSTANCE PREPARATION
The test substance was added to test water to give an initial stock solution of 99.6 mg test substance equivalents/L and ultrasonicated for approximately 90 minutes so that test substance was hydrolysed to MMBA. The pH of this stock solution was then adjusted using 0.5 mL 1N sodium hydroxide to a pH of 7.9. Serial dilutions of this stock solution were prepared with test water to give the desired series of exposure levels.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Strain: Straus
- Source: Cultured in-house and was obtained from a strain originating from the Institute National de Recherche Chimique Applique (IRChA), France.
- Age at study initiation (mean and range, SD): The day before the start of the study, all juvenile Daphnia were removed from the laboratory cultures. The following morning, juveniles produced by the gravid (egg-bearing) adult Daphnia were removed from the culture vessels and held in a separate holding vessel; these animals, which were less than 24 hours old, were used in the test.
- Method of breeding: Culture conditions ensured that cultures reproduce by parthenogenesis.
- Feeding during test: No.
ACCLIMATION
-Acclimation conditions: Stock cultures of Daphnia magna were maintained in glass vessels containing approximately 600 mL of Elendt M4 culture medium with a 16 hour light: 8 hour dark photoperiod at 20 ± 1 °C.
- Type and amount of food: Cultures were fed with a suspension of the unicellular green alga, Chlorella vulgaris.
- Feeding frequency: Daily.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
Test conditions
- Test temperature:
- 20 ± 1 °C
- pH:
- 7.2 - 7.9
- Dissolved oxygen:
- 7.9 - 9.3 mgO2/L
- Nominal and measured concentrations:
- Nominal test concentrations: 4.58, 9.96, 21.9, 45.8 and 99.6 mg test substance equivalents/L.
Mean measured test concentrations: 4.90, 10.7, 23.2, 46.6 and 100 mg test substance equivalents/L. - Details on test conditions:
- EXPOSURE CONDITIONS
Five duplicate concentrations were prepared including an untreated control. The test vessels were 250 mL capacity glass jars.
Ten first instar Daphnia were placed without conscious bias into glass jars, each containing 200 mL of prepared test medium or diluent medium to give a loading of 20 mL test solution per organism. The jars were loosely covered to minimise evaporative losses.
Daphnia were exposed to the test or control conditions for a period of 48 hours without renewal of test media.
ENVIRONMENTAL CONDITIONS
Photoperiod of 16 hours light: 8 hours dark and without supplementary aeration or feeding during the 48 hour exposure period.
The temperature in each vessel was measured daily and the pH and dissolved oxygen levels recorded at the start and at the end of the study.
CRITERION OF EFFECT
Daphnia were considered to be immobile if they were unable to swim within approximately 15 seconds following gentle agitation of the test vessel. - Reference substance (positive control):
- no
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 79.1 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% confidence limits (mg MMBC equivalents/L) 44.4 - 326
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 4.9 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- EVALUATION OF DATA
EC50 values were calculated using a logistic model (Berkson, 1944) for which 95% confidence limits were estimated by the likelihood ratio method (Williams, 1986).
Cumulative immobilisation data are given in Table 1. The test substance rapidly hydrolysed to MMBA with a half life of <15 minutes at 25°C in water. Based on this data, the compound in this study was initially converted to the hydrolysis product MMBA in order to test the compound up to a concentration of 99.6 mg test substance equivalents/L. The method of analysis investigated the concentration of MMBA, however, all results are expressed as the mean measured concentration of test substance equivalents (see Table 2). Measured concentrations ranged from 102 to 107% of nominal at 0 hours and 99.1 to 108% of nominal at 48 hours.
Analysis of the immobility data gave the following results:
Highest test concentration resulting in 0% immobilisation: < 4.90* mg test substance equivalents/L
Lowest test concentration resulting in 100% immobilisation: > 100 mg test substance equivalents/L
* 5% Daphnia immobilisation was observed at 48 hours in the control and the lowest test concentration. These levels of immobilisation are not considered to be biologically significant and therefore the no observed effect concentration (NOEC) is 4.90 mg test substance equivalents/L.
Any other information on results incl. tables
Table 1 Cumulative Immobilisation Data for Daphnia magna
Nominal Concentration (mg test substance equivalents/L) |
Mean Measured Concentration (mg test substance equivalents/L) |
Cumulative Immobilised Daphnia magna (initial population: 10 per replicate)
|
|||||||
24 hours |
48 hours |
||||||||
R1 |
R2 |
Total |
% |
R1 |
R2 |
Total |
% |
||
Control 4.58 9.96 21.9 45.8 99.6 |
Control 4.90 10.7 23.2 46.6 100 |
0 0 0 0 0 2 |
0 0 0 0 1 2 |
0 0 0 0 1 4 |
0 0 0 0 5 20 |
0 1 1 2 2 6 |
1 0 3 4 5 5 |
1 1 4 6 7 11 |
5 5 20 30 35 55 |
R1 Replicate 1
R2 Replicate 2
Table 2
Measured Concentrations - Mean Values and Percentages of Nominal
Nominal Concentration (mg test substance equivalents/L) |
Number of Samples Analysed |
Mean Measured Concentration (mg test substance equivalents/L) |
% Nominal |
Control 4.58 9.96 2 h9 45.8 99.6 |
2 2 2 2 2 2 |
None Detected 4.90 10.7 23.2 46.6 100 |
- 107 107 106 102 100 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The 48 h EC50 (immobilisation value) for the test substance with Daphnia magna was determined to be 79.1 mg test substance equivalents/L.
- Executive summary:
The acute toxicity of the test substance to aquatic invertebrates was investigated in Daphnia Magna in accordance with the standardised guidelines OECD 202 and EU Method C.2. Groups of twenty, first instar Daphnia, less than 24 hours old, were exposed to hydrolysed test substance for 48 hours at nominal concentrations of 4.58, 9.96, 21.9, 45.8 and 99.6 mg test substance equivalents/L dissolved in Elendt M4 medium (mean measured concentrations 4.90, 1037, 23.2, 46.6 and 100 mg test substance equivalents/L). The compound in this study was initially converted to the hydrolysis product MMBA in order to test the compound up to a concentration of 100 mg/L as required in the standard guidelines. The method of analysis investigated the concentration of MMBA, however, all results were expressed as the mean measured concentration of test substance equivalents. The numbers of immobilised daphnids was recorded for each test and control group after 24 and 48 hours. Under the conditions of the study, the 48 hour EC50 was determined to be 79.1 mg test substance equivalents/L.
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