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EC number: 434-440-3 | CAS number: -
- 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:
- 25 - 27 Aug 1998
- 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)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: All test concentrations and solvent control.
- Sampling method: At 0 h, additional duplicate vessels (280 mL) were prepared in an identical manner to those used in the test and their contents analysed. After 48 h, the contents of the vessels used in the test were analysed - Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: An aliquot (50 mg) of test substance was dissolved in 50 mL of ethanol to give an initial stock solution of 1 mg/mL. Serial dilutions of this stock solution were prepared with ethanol. Due to the volatility of the test substance (100% volatile by weight) an "air-free" test design was employed. Bottles of a total volume of 280 mL with air-tight screw caps, were filled to capacity with Elendt M4 medium and the caps secured. Each bottle was inverted and using a syringe to puncture a Teflon coated disc, located in the centre of the bottle cap, was spiked with 28 µL of the appropriate stock solution (to give a solvent loading equivalent to 100 µL/L). Each bottle was then shaken vigorously to aid dispersion.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): ethanol
- Controls: yes, test medium and solvent control
- Concentration of vehicle in test medium (stock solution and final test solution(s) or suspension(s) including control(s)): 100 µL/L - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Source: in-house culture, obtained from a strain originating from the Institute National de Recherche Chimique Applique (IRChA), France
- Age at study initiation: first instar; less than 24 h old (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 were used in the test)
- Method of breeding: Stock cultures of Daphnia magna were maintained in glass vessels containing approximately 800 mL of Elendt M4 culture medium with a 16 h light: 8 h dark photoperiod at 20 ± 2 °C. Cultures were fed daily with a suspension of the unicellular green alga, Chlorella vulgaris. Culture conditions ensure that cultures reproduce by parthenogenesis.
- Feeding during test: none - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Test temperature:
- 19 °C (at test start and end)
- pH:
- 7.5 - 8.3 (at test start)
6.7 - 7.3 (at test end) - Dissolved oxygen:
- 7.4 - 9.0 mg O2/L (at test start)
6.1 - 8.0 mg O2/L (at test end) - Nominal and measured concentrations:
- control, solvent control, 0.10, 0.22, 0.46, 1.0, 2.2, 4.6, 10 and 22 µg/L (nominal)
not detected, < LOQ,- Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Type: closed (by aid of air-tight screw caps)
- Material, size, headspace, fill volume: 280 mL glass bottles filled to capacity with no headspace
- Aeration: none
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- No. of vessels per vehicle control (replicates): 4 (containing 100 µL solvent/L)
- Biomass loading rate: 56 mL test solution per organism
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Elendt M4 medium
Trace elements (mg/L):
H3BO3: 2.86
MnCl2.4H2O: 0.36
LiCl: 0.31
RbCl: 0.071
SrCl2.6H2O: 0.152
NaBr: 0.016
Na2MoO4.2H2O: 0.063
CuCl2.2H2O: 0.017
ZnCl3: 0.013
CoCl2.6H2O: 0.010
KI: 0.0033
Na2.SeO3: 0.0022
NH4VO3: 0.00058
Fe-EDTA solution: 3.50
Macro nutrients (mg/L):
CaCl2.2H2O: 294
MgSO4.7H2O: 123
KCl: 5.80
NaHCO3: 64.8
Na2.SiO3.9H2O: 10.0
NaNO3: 0.274
KH2PO4: 0.143
K2HPO4: 0.184
Vitamins (mg/L):
Thiamine hydrochloride: 0.075
Cyanocobalamine (Vitamin B12): 0.0010
Biotin (Vitamin H): 0.00075
- Culture medium different from test medium: no
- Intervals of water quality measurement: temperature, pH, and dissolved oxygen levels were recorded in each vessel at the start and the end of the study
OTHER TEST CONDITIONS
- Photoperiod: 16h light / 8 h dark
EFFECT PARAMETERS MEASURED: Immobilisation, observed at 24 and 48 h
TEST CONCENTRATIONS
- Spacing factor for test concentrations: approx. 2.2
- Range finding study: yes
- Test concentrations: 0.01 to 100 µg/L
- Results used to determine the conditions for the definitive study: The NOEC was approximately 0.1 µg/L and the LOEC resulting in 100% immobilisation was approximately 100 µg/L.- Reference substance (positive control):
- no
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.007 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CL: 0.0032 - 0.015 mg/L
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Immobilisation of control: 5% (test medium control), 0% (solvent control)
- Reported statistics and error estimates:
- EC50 values and 95% confidence limits were calculated using the Thompson and Weil model (Thompson, W.R. and Weil, C.S. (1952) Biometrics 8: 51 -54).
Analytical measurements:
Analysis of the 4.6, 10 and 22 µg/L test concentrations gave measured concentrations ranging from 144 - 107% of nominal at 0 hours and 91 - 83% of nominal at 48 h. Due to the limited sensitivity of the method of analysis (limit of quantification >4 µg/L) it was not possible to verify the aqueous test concentrations below 4.6 µg/L. However, the stock solutions used to prepare all the exposure concentrations were analysed and found to be 97 - 72% of nominal at 0 h, so it is reasonable to infer that near nominal concentrations were achieved at the start of the study.
Table 1: Cumulative immobilisation of Daphnia exposed for 48 hours
Nominal concentration [µg/L]
Geometric mean measured concentration [µg/L]
Cumulative immobilised Daphnia magna (initial population: 5 per replicate)
24 h
48 h
R1
R2
R3
R4
Total
%
R1
R2
R3
R4
Total
%
Control
-
0
0
0
0
0
0
0
0
0
l
1
5
Solvent Control
ND
0
0
0
0
0
0
0
0
0
0
0
0
0.10
*
0
0
0
0
0
0
1
1
0
0
2
10
0.22
*
0
0
0
0
0
0
0
0
0
1
1
5
0.46
*
0
0
0
1
1
5
0
1
0
2
3
15
1.0
*
0
0
0
2
2
10
1
0
0
3
4
20
2.2
*
0
0
1
0
1
5
1
0
2
2
5
25
4.6
5.1
1
1
1
0
3
15
J
3
2
2
10
50
10
9.5
1
1
3
2
7
35
5
2
3
2
12
60
22
22
2
1
2
3
8
40
4
2
5
5
16
80
R1 -R4: Replicate No.
*: Below limit of quantification of 4 µg/L
ND: None detected
Tables 2 to 5: Summary of analytical chemistry results
Table 2: Analytical results
Occasion
Nominal concentration [µg/L]
Measured concentration [µg/L]
Expressed as a percentage of nominal
0 h
Control
ND
-
4.6
6.634
144
10
10.94
109
22
23.59
107
48 h
Control
ND
-
4.6
3.924
85.3
10
8.328
83.3
22
20.04
91.1
Table 3: Stock solutions
Nominal concentration [mg/mL]
Measured concentration [mg/mL]
Expressed as a percentage of nominal
1.0
0.7207
72.1
2.2
1.669
75.9
4.6
4.193
91.2
10
9.246
92.5
22
20.66
93.9
46
43.69
95.0
100
97.43
97.4
220
200.1
91.0
1000
954.8
95.5
Table 4: Procedural recoveries (test levels)
Occasion
Fortified concentration (µg/L)
Recovery as a percentage of fortified
0 h
Control
ND
10.88
92.9
10.88
93.9
48 h
Control
ND
10.88
91.9
10.88
94.8
Mean (RSD)
93.3 (1.3)
Table 5: Procedural recoveries (stock levels)
Fortified concentration (mg/mL)
Recovery as a percentage of fortified
21.76
101
21.76
97.7
Mean
99.1
Reference
Description of key information
EC50 (48 h): 0.0068 mg/L (nominal, OECD 202)
Key value for chemical safety assessment
Additional information
One experimental study is available investigating the short-term effects of the substance to aquatic invertebrates (Cytec Industries, 1998). The study was performed according to OECD 202 (GLP) using Daphnia magna as test organism. A stock solution of 100 mg/L was prepared in ethanol to prepare the final nominal test solutions of 0.10, 0.22, 0.46, 1.0, 2.2, 4.6, 10 and 22 µg/L. In addition a test medium control and solvent control were tested. The actual test concentrations were measured by GC/FID analysis. Since the Limit of Quantification was < 4 µg/L only the three highest concentrations could be analysed. The analysis resulted in a mean concentration of 5.1, 9.5, and 22 µg/L (compared to nominal 4.6, 10 and 22 µg/L). Thus, the substance is considered to be stable under testing conditions. Immobilisation of Daphnids was observed resulting in an EC50 (48 h) of 0.0068 mg/L (95% CI: 0.0032 - 0.015 mg/L) based on nominal concentrations.
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