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EC number: 213-537-2 | CAS number: 971-15-3
- 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:
- 03-22-2017 to 04-12-2017
- 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:
- yes
- Remarks:
- The temperature for the study was slightly higher than stated in the guideline. As no immobility in the blank control occurred during the test and all validity criteria were fulfilled, this deviation was stated as uncritical.
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Remarks:
- Due to the test items properties, the study was performed without analytical determination of the test item.
- Vehicle:
- yes
- Remarks:
- Because of the very low solubility of the test item, acetone was used to spike the test solutions.
- Details on test solutions:
- During validation of the analytical method in spiked solutions at the concentration of 10 µg/L (taken as limit of water solubility) in test medium, no test item was detectable. That means solubility in test medium is much lower than in demineralised water. Development of an analytical method for measurement of test item in test medium was not possible.
Because test item is not measurable, in agreement with the OECD guidance document no. 23, no analytical determination of the test item in the test solutions was made in this study and the effects were based on nominal concentrations.
The solubility in water is stated as 10.48 µg/L (MSDS, provided by the sponsor). In this study, the limit of water solubility was used as highest concentrated treatment. Because of the very low solubility of the test item, acetone was used to spike the test solutions. Stock solutions containing 105 mg/L nominal concentration (real load 105 – 115 mg/L) and 5 mg/L of test item (prepared from the 105 mg/L stock solution) were prepared in acetone. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Species Daphnia magna
Variety STRAUS
Arrival of Strain 27. Sep. 2007
Sex female
Age between 0 and 24 hours
The animals which were used in the test did not belong to the first brood of the respective parent animals.
ANIMAL HUSBANDRY
Daphnia magna is bred in the LAUS GmbH throughout the year. The animals were originally obtained from the Umweltbundesamt in Berlin and are kept for the use in toxicity tests. They multiply by parthenogenesis, thus being genetically identical. The husbandry is performed similar to the method described in the OECD guideline, following SOP 115 002 01 (“Zucht und Hälterung von Daphnia magna STRAUS“), edition 12, adopted 02. Feb. 2015.
Vessels glass beakers, nominal volume 2 L
Medium M4-Medium (recipe of ELENDT)
Food green alga (Desmodesmus subspicatus)
Medium renewal twice a week
Photo period 1 6/8 hours, using neon tubes
Temperature 20 +/-2 °C - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 21 d
- Hardness:
- 267 - 356 mg CaCO3/L
- Test temperature:
- 19.4 – 22.4°C
- pH:
- 7.7 - 8.0
- Dissolved oxygen:
- 8.5 - 9.5
- Salinity:
- Freshwater
- Nominal and measured concentrations:
- Nominal concentrations: 0 - 5 - 10.5 µg/L
- Details on test conditions:
- Duration 21 days
Loading 80 mL/animal, animals were kept individually
Replicates 10 replicates/treatment
Treatments 10.5 and 5 µg/L
Blank Control dilution water
Solvent Control 100 µL acetone / L dilution water
Lighting 1000 Lux
Aeration none
Feeding unicellular green algae Desmodesmus subspicatus: 0.15 - 0.20 mg organic carbon/animal/day, the amount of carbon is based on photo metric measurement (linear cor-relation between absorption at 440 nm and measured DOC concentration). - Reference substance (positive control):
- no
- Key result
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 10.5 µg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Remarks on result:
- other: No effect up to solubility limit
- Key result
- Duration:
- 21 d
- Dose descriptor:
- LOEC
- Effect conc.:
- > 10.5 µg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Details on results:
- Calculation of results was performed with the help of validated software (Microsoft Excel®). The estimation of the biological results was accomplished using the software Tox-Rat® Professional, version 3.2.1. The number of offspring in the solvent control was slightly higher than in the blank control but the difference between the control and the solvent control was not significant. Therefore, in agreement with the OECD guideline, for statistical evaluation, all blank control and solvent control replicates were pooled.
- Validity criteria fulfilled:
- yes
- Conclusions:
- One valid experiment was performed according to OECD 211 Guideline in order to evaluate the effect of test item on the reproduction of Daphnia magna.
RESULTS:
Based on nominal concentrations,
NOEC = 10.5 µg/L
LOEC > 10.5 µg/L
VALIDITY CRITERIA:
All validity criteria were met.
PARAMETER DEMANDED VALUE FOUND VALUE
Mortality of parent animals in the blank control < 20 % 0 %
Mean surviving offspring in the blank control > 60 101
Mortality of parent animals in the solvent con-trol < 20 % 10 %
Mean surviving offspring in the solvent control > 60 109
O2 concentration > 3 mg/L = 8.5 mg/L
pH range 6 – 9 7.7 - 8.0
pH variation < 1.5°C 0.3°C
Temperature 18°C - 22°C, 19.4°C – 22.4°C
variation = 2.0 units variation of 3.0 units
The temperature and the range of the temperature was slightly higher than stated in the study plan (22.4 °C instead of 22.0°C, difference 3 °C instead of = 2.0 °C) . Because no mortality above the validity criteria and no abnormal behaviour was observed in the controls, this can be stated as uncritical. - Executive summary:
One valid experiment was performed according to OECD 211 Guideline in order to evaluate the effect of test item on the reproduction of Daphnia magna.
The solubility in water was considered as 10.48 µg/L (see OECD 105 study included in the present REACh dossier). In this study, the limit of water solubility was used as highest concentrated treatment. The study was performed using the concentrations 10.5 µg/L and 5 µg/L. Because of the very low solubility of the test item, acetone was used to spike the test solutions. Therefore a solvent control was prepared in addition to the blank control (solvent concentration: 0.1 mL/L).
For each control and test item treatment, ten daphnia were exposed for 21 days.
Medium renewal was performed every day to maximize exposure of the test organism to the test item. The offspring of the animals was counted every day.
Significant decrease in the reproduction of the daphnia was not observed in the treatments.
During validation of the analytical method in spiked solutions at the concentration of 10 µg/L (taken as limit of water solubility) in test medium, no test item was detectable. That means solubility in test medium is much lower than in demineralised water. Development of an analytical method for measurement of test item in test medium was not possible.
Because test item is not measurable, in agreement with the OECD guidance document no. 23, no analytical determination of the test item in the test solutions was made in this study and the effects were based on nominal concentrations.
The following results were determined for the test item:
NOEC >=10.5 µg/L
LOEC > 10.5 µg/L
Reference
Table 1: Offspring
Replicate No. |
Blank Control |
Solvent Control |
5 µg/L |
10.5 µg/L |
1 |
105 |
112 |
120 |
86 |
2 |
112 |
125 |
90 |
106 |
3 |
109 |
M |
M |
113 |
4 |
119 |
112 |
118 |
M |
5 |
114 |
101 |
119 |
93 |
6 |
104 |
112 |
100 |
111 |
7 |
95 |
121 |
104 |
72 |
8 |
66 |
107 |
90 |
M |
9 |
97 |
98 |
102 |
72 |
10 |
86 |
90 |
99 |
112 |
Mean |
101 |
109 |
105 |
96 |
SD |
16 |
11 |
12 |
17 |
RSD |
16 |
10 |
11 |
18 |
SD = standard deviation;
RSD = relative standard deviation = coefficient of variation
M = mortality of parent animal
Table 2: Fecundity
Treatment |
Total Offspring |
Surviving Parent Animals |
Mean Offspring per Surviving Parent Animal |
Blank Control |
1007 |
10 |
101 |
Solvent Control |
978 |
9 |
109 |
5 µg/L |
942 |
9 |
105 |
10.5 µg/L |
765 |
8 |
96 |
Description of key information
Key value for chemical safety assessment
Additional information
One valid experiment was performed according to OECD 211 Guidelinein order to evaluate the effect of test item on the reproduction ofDaphnia magna.
The solubility in water was stated as 10.48 µg/L. In this study, the limit of water solubility was used as highest concentrated treatment. The study was performed using the concentrations 10.5 µg/L and 5 µg/L. Because of the very low solubility of the test item, acetone was used to spike the test solutions. Therefore a solvent control was prepared in addition to the blank control (solvent concentration: 0.1 mL/L). For each control and test item treatment, ten daphnia were exposed for 21 days. Medium renewal was performed every day to maximize exposure of the test organism to the test item. The offspring of the animals was counted every day.
Significant decrease in the reproduction of the daphnia was not observed in the treatments. It is concluded that no adversed effect was detected up to the water solubility limit of DPTH.
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