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EC number: 205-463-4 | CAS number: 141-16-2
- 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:
- 19 May - 26 July 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- Adopted 13 April, 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 30 May 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Swiss Federal Office for the Environment
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: each test concentration and the control
- Sampling method: duplicate samples at the start and end of the two 24-hour test medium renewal periods
- Sample storage conditions before analysis: Immediately after sampling, acetonitrile (6 mL acetonitrile per 9 mL sample volume) was added to each sample for stabilization; storage at -20°C - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: stirring/filtration: The test item was mixed in test water at a loading rate of 100 mg/L, and was intensively stirred for 3 hours. After stirring the emulsion was filtered through a 0.45 μm membrane filter. The undiluted filtrate and the dilutions 1:2.2, 1:4.6, 1:10, and 1:22 of the filtrate were used as test media.
- Controls: blank water control - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain/clone: Daphnia magna Straus
- Feeding during test: no feeding - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 250 mg CaCO3/L
- Test temperature:
- 21 °C
- pH:
- 7.7 - 7.8 (control)
7.6 - 8.0 (test concentrations) - Dissolved oxygen:
- 8.2 - 8.5 mg/L (control)
7.9 - 8.5 mg/L (test concentrations) - Nominal and measured concentrations:
- nominal: control, 1:22 dilution, 1:10 dilution, 1:4.6 dilution, 1:2.2 dilution, undiluted filtrate (loading rate of 100 mg/L)
measured (arithmetic mean): < 0.069 mg/L, n/a, n/a, 0.12 mg/L, 0.32 mg/L, 0.74 mg/L - Details on test conditions:
- TEST SYSTEM
Test vessel:
- Type: closed
- Material, size, headspace, fill volume: glass vessels completely filled (without headspace) with 60 mL test medium and tightly sealed with glass stoppers
- Renewal rate of test solution: test medium renewal after 24 hours
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 20
- No. of vessels per control (replicates): 20
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: test item was diluted with test water which was prepared according to OECD Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures, 2000
- Ca/Mg ratio: 4:1
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Photoperiod: 16 h light / 8 h dark with 30 min transition period
- Light intensity: 15 - 18 μmol m-2 s-1.
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : immobility at 24 and 48 h
RANGE-FINDING STUDY
- Test concentrations: control, dilution 1:20, dilution 1:5, undiluted filtrate (undiluted filtrate with loading rate of 100 mg/L)
- Results used to determine the conditions for the definitive study: test concentrations and test media preparation in definitive test based on range-finding study - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.41 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CI: 0.32 - 0.53 mg/L
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 0.12 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 0.74 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.12 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Mortality of control: none
- Other adverse effects control: none
- Abnormal responses: none
- Other: Biological and analytical results are summarized within the section "Any other information on results incl.tables" - Results with reference substance (positive control):
- - Results with reference substance valid? yes; potassium dichromate is tested as a positive control twice a year
- EC50 (24h): 1.6 mg/L (range given by test guideline: 0.60-2.1 mg/L) - Reported statistics and error estimates:
- The 24-hour EC50 could not be calculated due to the low toxicity of the test item (25% immobility at the highest test concentration). The 48-hour EC50 was calculated by Probit Analysis using linear maximum likelihood regression.Statistical analysis was performed using ToxRat Professional®. The 24-hour and 48-hour NOEC, EC0 and EC100 were determined directly from the raw data.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The test item had acute toxic effects in a 48-hour semi-static test based on immobility of Daphnia magna with an EC50 (48 h) value of 0.41 mg/L (arithmetic mean measured concentration) (OECD 202, GLP).
Reference
Table 1: Effect of the test material on the mobility of Daphnia magna
Treatment / Dilution
|
Mean measured concentration [mg/L] |
No. of daphnids tested
|
Immobilized daphnids after 24 hours |
Immobilized daphnids after 48 hours |
||
No. |
[%] |
No. |
[%] |
|||
Control |
-- |
20 |
0 |
0 |
0 |
0 |
Dilution 1:22 |
n.a |
20 |
0 |
0 |
0 |
0 |
Dilution 1:10 |
n.a |
20 |
0 |
0 |
0 |
0 |
Dilution 1:4.6 |
0.12 |
20 |
0 |
0 |
0 |
0 |
Dilution 1:2.2 |
0.32 |
20 |
0 |
0 |
7 |
35 |
Undiluted Filtrate* |
0.74 |
20 |
5 |
25 |
17 |
85 |
n.a.: Not analyzed since below the NOEC determined in this test
*: Undiluted filtrate with a loading rate of 100 mg/L
Table 2: ECx values based on mean measured test item concentrations
ECxValues |
Immobility Mean measured concentration [mg/L] |
24-hour EC50 |
>0.74 |
24-hour EC0 |
0.32 |
24-hour EC100 |
>0.74 |
48-hour EC50 |
0.41 |
(95%-confidence limits) |
(0.32 – 0.53) |
48-hour EC0and 48-hour NOEC |
0.12 |
48-hour EC100 |
>0.74* |
*: At the undiluted filtrate, 85% of the daphnids were found to be immobile.
Table 3: Analytical Results for Test Samples
Sampling Day / Age of Sample |
Dilution Factor of Filtrate of Loading Rate 100 mg Test Item /L |
Measured Concentration of Test Item x |
Sample Preparation Factor
F |
Determined Concentration of Test Item c |
% of Initially Measured Concentration |
[d/h] |
|
[mg/L] |
|
[mg/L] |
|
0/0 |
Control |
n.d. |
1.667 |
<LOQ |
|
(fresh) |
1:4.6-Dilution |
0.116 |
1.667 |
0.193 |
|
|
1:2.2-Dilution |
0.247 |
1.667 |
0.412 |
|
|
Undiluted Filtrate |
0.572 |
1.667 |
0.954 |
|
0/24 |
Control |
n.d. |
1.667 |
<LOQ |
n.a. |
(aged) |
1:4.6-Dilution |
0.051 |
1.667 |
0.084 |
44% |
|
1:2.2-Dilution |
0.147 |
1.667 |
0.246 |
60% |
|
Undiluted Filtrate |
0.410 |
1.667 |
0.683 |
72% |
1/0 |
Control |
n.d. |
1.667 |
<LOQ |
|
(fresh) |
1:4.6-Dilution |
0.093 |
1.667 |
0.156 |
|
|
1:2.2-Dilution |
0.243 |
1.667 |
0.405 |
|
|
Undiluted Filtrate |
0.563 |
1.667 |
0.939 |
|
2/24 |
Control |
n.d. |
1.667 |
<LOQ |
n.a. |
(aged) |
1:4.6-Dilution |
0.051 |
1.667 |
0.085 |
55% |
|
1:2.2-Dilution |
0.152 |
1.667 |
0.253 |
63% |
|
Undiluted Filtrate |
0.288 |
1.667 |
0.480 |
51% |
LOQ: 0.069 mg/L
n.d. = not detected
n.a. = not applicable
Table 4: Mean measured Concentrations based on Analytical Results
Treatment/ Dilution |
Measured Test Item Concentations at the Start of the Renewal Periods (Day 0/Day 1) |
Measured Test Item Concentations at the End of the Renewal Periods (Day 1/Day 2) |
Mean Measured Concentration of the Test Item |
[mg/L] |
[mg/L] |
[mg/L] |
|
Dilution 1:22 |
n.a. |
n.a. |
n.a. |
Dilution 1:10 |
n.a. |
n.a. |
n.a. |
Dilution 1:4.6 |
0.19 / 0.16 |
0.084 / 0.085 |
0.12 |
Dilution 1:2.2 |
0.41 / 0.41 |
0.25 / 0.25 |
0.32 |
Undiluted Filtrate* |
0.95 / 0.94 |
0.68 / 0.48 |
0.74 |
*: Undiluted filtrate with a loading rate of 100 mg/L
n.a.: Not analyzed since below the NOEC determined in this test
Description of key information
EC50 (48 h) = 0.41 mg/L (arithmetic mean measured concentration, OECD 202, Daphnia magna)
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.41 mg/L
Additional information
There is one GLP guideline study available, which assessed the effects of substance towards aquatic invertebrates (Daphnia magna) according to the OECD guideline 202. As the test item is a volatile substance, the test was performed using glass tubes completely filled with test medium that were tightly sealed with glass stoppers to avoid losses of test item by evaporation. A semi-static test design with a test medium renewal after 24 hours was used. Due to the low water solubility of the test item, the test media were prepared following the filtration method. Therefore the test item was mixed in test water at a loading rate of 100 mg/L, and was intensively stirred for 3 hours. After stirring the emulsion was filtered through a 0.45 μm membrane filter. The undiluted filtrate and the dilutions 1:2.2, 1:4.6, 1:10, and 1:22 of the filtrate were used as test media. The concentration range was previously established in a preliminary range-finding test. The loading rates of the test item were analytically verified by HPLC-UV. At the end of the two renewal periods, the test item concentration were in a range of 44 to 72 % of the initially measured values, demonstrating a decrease of the test item concentrations during the 24-hour renewal periods. The mean measured test item concentrations were calculated as the arithmetic mean of the two geometric means. The EC50 (48 h) value was 0.41 mg/L.
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