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Diss Factsheets
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EC number: 204-616-2 | CAS number: 123-30-8
- 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
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- March 21 to April 16, 1997
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Test procedure in accordance with generally accepted scientific standards and described in sufficient detail
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- HLPC at the start of exposure, 3 hours and 24 hours afterwards. Sample was taken from the middle section of each test solution.
- Vehicle:
- no
- Details on test solutions:
- Based on preliminary work that preceded this study, the maximum testing concentration was set at 1.00 mg/L (considered 100% immobilisation concentration). 5 concentrations were established with a common ratio of 1.8 ( 1.00, 0.556, 0.309, 0.171 and 0.0953 mg/L).
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- juvenile daphnia born no later than 24 hours beforehand were used. Species bred and rasied from supply from EPA Laboratory USA.
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- test solution changed after 24 hours
- Hardness:
- 55.6 mg/l as CaCO3
- Test temperature:
- 20.0-20.2 C
- pH:
- 7.6-7.7
- Dissolved oxygen:
- 8.6 to 8.8 mg/l
- Salinity:
- 37.5 mg/l
- Nominal and measured concentrations:
- measured concentrations of the test article were 103-106% of the labeled concentrations at the start of exposure, 51.4 % -65.3% after 3 hours ad 0.0to14.0% at the time the solution was changed (24 hours).
- Details on test conditions:
- see below
- Reference substance (positive control):
- no
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.089 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- act. ingr.
- Remarks:
- arithmatic mean of the first 24 h and measures at t=0. 3 and 24h; RR 6% after 24 hours
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CL; Values based on mean measured concentrations calculated directly from data in the study report.
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.064 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- Values based on mean measured concentrations calculated directly from data in the study report.
- Reported statistics and error estimates:
- see below
- Validity criteria fulfilled:
- yes
- Conclusions:
- EC50 at 48 hours was 0.182 mg/l for nominal measured concentration. Nominal NOEC at 48 hours was 0.177 mg/L and LOEC 0.313 mg/L for nominal measured concentrations. Values based on mean measured concentrations calculated directly from data in the study report.
The substance degrades very fast in the test with a (>65% loss after 24hr) therefore results are expressed as the mean goemetric mean values which would result in a LD50 of 0.089 mg/L. Based on the tables it would seem that the gemoetric mean NOEC value in this instance would be 0.064 mg/L
Reference
- Measured
Concentrations: The test concentrations were measured three times (0, 3,
24th hour) during the test period using HPLC.
Nominal Conc. (mg/L) | Measured Concentration (mg/L) | Geometric mean* | ||
0 hour | 3 hour | 24 hours | ||
Control | n.d. | n.d. | n.d. | --- |
0.0953 | 0.0979 | 0.0622 | n.d. | 0.024 |
0.171 | 0.177 | 0.111 | 0.0240 | 0.065 |
0.309 | 0.329 | 0.174 | 0.0243 | 0.089 |
0.556 | 0.588 | 0.286 | 0.0376 | 0.15 |
1.00 | 1.04 | 0.522 | n.d. | 0.077 |
n.d.: <0.00567 mg/L
*: Geometric mean of measured concentration at the initial and 24th-hour (before water replacement).
Nominal Conc. (mg/L) | % of Nominal concentration (%) | |||
0 hour | 3 hour | 24 hours | Geometric mean | |
Control | --- | --- | --- | --- |
0.0953 | 103 | 65.3 | --- | 25.2 |
0.171 | 104 | 65.0 | 14.0 | 38.0 |
0.309 | 106 | 56.4 | 7.9 | 28.8 |
0.556 | 106 | 51.4 | 6.8 | 27.0 |
1.00 | 104 | 52.2 | --- | 7.7 |
-
Water chemistry (pH, DO, and temperature in test): Water chemistry and
temperature were measured for control and each concentration at the
start and before water replacement (24th-hour) of the test.
pH: 7.6 - 7.7
DO: 8.6 - 8.8 mg/L
Water Temperature: 20.0 - 20.2 C
-Effect Data:
EC50 (48hr) 0.182mg/L (mc)
95% Confidence Interval: 0.085 – 0.11 mg/L
mc: based on measured concentrations
-Mortality
or Immobility: None of test organisms were immobilized the behaviours at
control.
Nominal Conc. (mg/L) | Measured Conc. (mg/L) | Cumulative Number of Immobilized Daphnia (Percent Immobility, %) | |||
24 hour | (%) | 48 hours | (%) | ||
Control | --- | 0 | 0 | 0 | 0 |
0.0953 | 0.024 | 0 | 0 | 1 | 5 |
0.171 | 0.065 | 0 | 0 | 1 | 5 |
0.309 | 0.089 | 4 | 20 | 10 | 50 |
0.556 | 0.15 | 14 | 70 | 17 | 85 |
1.00 | 0.077 | 17 | 85 | 20 | 100 |
Description of key information
The short-term toxicity in daphnia magna is from one key study with results calculated as mean measured concentrations of EC50 (48 hours) 0.089 mg/l and NOEC of 0.064 mg/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.089 mg/L
Additional information
The key study is an Acute Toxicity in Daphnia magna completed in 1997 based on OECD method 202 with a reported EC50 (48 hours) mean measured values as 0.0.089mg/l, NOEC as 0.064 mg/L. Values were based on mean measured concentrations calculated directly from data in the study report. The measured concentrations of the test article were 103 -106% of the labeled concentrations at the start of exposure, 51.4 % -65.3% after 3 hours and 0.0 to14.0% at the time the solution was changed (24 hours). One supporting study was included with klimisch of 4: daphnia magna - EC50 (48 h): 0.24 mg/L. As the substance degrades rapidly an additional study was conducted to determine the toxicity of the degradation products versus the parent molecule. The results of this study show that the parent molecue is significanty more toxic that the degradation products.
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