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EC number: 947-751-9 | 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:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- From January 02, 2018 to January 04, 2018
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- KL2 due to RA
- Justification for type of information:
- Refer to section 13 of IUCLID for details on the read-across justification. The study with the read across substance is considered sufficient to fulfil the information requirements as further explained in the provided endpoint summary.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- not specified
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Remarks:
- High-performance liquid chromatography (HPLC)
- Details on sampling:
- To demonstrate that nominal exposure concentrations were being achieved the concentrations of test substance in the test vessels were measured using the high-performance liquid chromatography method. At study start, samples were taken from excess test solutions and at study end from the test vessels of the dilution water control, solvent control and each test concentration.
- Vehicle:
- yes
- Remarks:
- Water
- Details on test solutions:
- The study was run with a dilution water control and nominal exposure concentrations of 0.625, 1.25, 2.5, 5 and 10 mg/L. A primary stock concentrate of Test substance, with a nominal concentration of 10 mg/L, was prepared by adding a nominal 0.020 g of test substance (actual weight 0.02015 g) and making up to 2000 mL volume with dilution water in a volumetric flask. The stock was sonicated for 45 minutes and the resultant stock observed to be a homogenous, colourless dispersion with fine particles visible. The stock was used directly as the 10 mg/L test solution and used to prepare the other test solutions by the direct addition of the appropriate amount to dilution water in a volumetric flask. The control consisted of dilution water only. All test solutions were clear and colourless. In all cases the final solutions contained nutrients.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- The test organism was the freshwater crustacean, Daphnia magna, obtained from continuous laboratory cultures held at Scymaris. The stock cultures of D. magna were maintained in a reconstituted water medium, the same as the test dilution water, at a temperature of 20 ± 2°C. The cultures were maintained in 2 L glass vessels with a working volume of 1.6 L. A photoperiod of 16 h light:8 h dark, with 20-minute transition periods was provided. The D. magna cultures were fed on a mixed algae diet of Chlorella vulgaris, strain CCAP 211/12 and Pseudokirchneriella subcapitata, strain CCAP 278/4. The D. magna cultures were fed a daily ration depending on the age and density of the culture. Culture conditions were such that the D. magna reproduction was by diploid parthenogenesis. D. magna <24 h old, obtained from a single culture vessel, were used for testing. The parent animals were 28 ± 1 d old and had been maintained with a twice weekly renewal of reconstituted water medium since birth. The test organisms and the culture from which they were obtained showed no evidence of disease before the test period.
- Test type:
- static
- Water media type:
- other: Elendt's M4 D. magna medium
- Limit test:
- no
- Total exposure duration:
- 48 h
- Test temperature:
- 20±1°C
- pH:
- 7.92 to 8.03
- Dissolved oxygen:
- 8.97 to 9.44 mg/L
- Nominal and measured concentrations:
- Control and 0.625, 1.25, 2.5, 5 and 10 mg/L (nominal)
Control and 0, 0, 0, 0.21 and 0.34 mg/L (measured)
A 10 mg/L test concentration was selected as the highest concentration based on the dispersibility observed in a non-GLP range finding test - Details on test conditions:
- Apparatus
Glass beakers of 250 mL nominal capacity were used as test vessels, with four replicates per test concentration. Each vessel contained 200 mL of test solution providing a depth of approximately 60 mm. The beakers were covered with loose fitting glass lids. The positions of the treatments were randomly allocated within the test area. - Reference substance (positive control):
- no
- Key result
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 0.34 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat. (total fraction)
- Basis for effect:
- mobility
- Remarks on result:
- other: Calculation method: Direct observation from data
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 0.34 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat. (total fraction)
- Basis for effect:
- mobility
- Remarks on result:
- other: Calculation method: Direct observation from data
- Key result
- Duration:
- 48 h
- Dose descriptor:
- LOEC
- Effect conc.:
- ca. 0.34 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat. (total fraction)
- Basis for effect:
- mobility
- Key result
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- > 0.34 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat. (total fraction)
- Basis for effect:
- mobility
- Details on results:
- Analytical data
The limit of quantification (LOQ) in this study was 0.4 mg/L for all test solutions. The instrument LOQ was 0.2 mg/L but during analysis, samples from the control and each test concentration were diluted x2, doubling the LOQ. Analytical calibrations were constructed using a minimum of 5 calibration levels, with a minimum R2 value of 0.995. The maximum percentage difference from nominal concentration for standards at the LOQ is less than 20% and less than 15% at levels greater than the LOQ. All analytical values are quoted to two significant figures and percentages to the nearest integer. On the basis of the analytical data the mean measured concentrations were used for the calculation and reporting of results.
Biological data
Based on immobility compared to the control (p <0.05) the 48 h No Observed Effect Concentration (NOEC) was determined to be 0.34mg/L and the Lowest Observed Effect Concentration (LOEC) was >0.34 mg/L. There was no immobility observed in the dilution water control. No other symptoms of toxicity were observed. It was observed that test substance was visible on the surface of the test vessels as a raft of fine particles at 24 h and 48 h in a dose dependant amount. - Validity criteria fulfilled:
- yes
- Conclusions:
- Based on the results of read across study, the 48 h EC50 of the test substance for Daphnia magna is considered to be >0.34 mg/L (measured).
- Executive summary:
A study was conducted to determine the acute toxicity of read across substance, mono- and di- C16 PSE, K+ and H3PO4 (100%), to Daphnia magna, according to the OECD Guideline 202, in compliance with GLP. Twenty test organisms were exposed to each nominal read across substance concentrations of 0, 0.625, 1.25, 2.5, 5 and 10 mg/L for 48 h under static conditions. The concentrations of read across substance in the test vessels were measured using the high-performance liquid chromatography method. The mean measured concentrations of read across substance were determined to be 0, 0, 0, 0, 0.21 and 0.34 mg/L. Immobilisation was recorded at 24 and 48 h and compared with control values. Based on immobility compared to the control (p <0.05), the 48 h NOEC was determined to be 0.34 mg/L (measured) and the LOEC was >0.34 mg/L (measured). No other symptoms of toxicity were observed. Based on the study results, the 48 h EC50 was calculated to be >0.34 mg/L (measured). As no immobility or other signs of stress were observed in the control and dissolved oxygen concentration remained at ≥3 mg/L, this test has satisfied all validity criteria. Under the study conditions, the 48 h EC50 of the read across substance for Daphnia magna was determined to be >0.34 mg/L(measured) (Scymaris, 2018). Based on the results of the read across study, similar EC50 and NOEC values can be expected for the test substance, 'mono- and di- C16 PSE, K+ and C16-OH and isostearyl isostearate'.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- 1998
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- KL2 due to RA
- Justification for type of information:
- Refer to section 13 of IUCLID for details on the read-across justification. The study with the read across substance is considered sufficient to fulfil the information requirements as further explained in the provided endpoint summary.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- other: EU guideline 92/69/EWG
- Deviations:
- not specified
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Remarks:
- Fluid chromatography of dichloromethane extract
- Vehicle:
- no
- Details on test solutions:
- Concentrations: 10, 30, 100, 1000, 3000 mg/L
Renewal of test solution: None
Exposure vessel type: 100 mL beakers covered with clockglasses - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Test organism
Strain: Daphnia magna
Supplier: BioInternational B.V., NJ Horn, NL
Age: 6-24 h old
Feeding: Green algae during 6 hours prior to testing
Pretreatment: M4 medium / 20oC / 16h light - 8h dark
Feeding during test: No feeding according to EU guideline
Control group: 1 group (2 replicates)
Number of replicates: 2
Invertebrate per replicate: 10 - Test type:
- static
- Water media type:
- other: Water accommodated fractions
- Limit test:
- no
- Total exposure duration:
- 48 h
- Test temperature:
- 20.8-20.9 deg C
- pH:
- mean pH: 7.9
- Dissolved oxygen:
- 99.2%
- Nominal and measured concentrations:
- 0, 10, 30, 100, 1000, 3000 mg/L nominal Water accommodated fractions (WAF)
Measured concentrations of C12, C14, C16 and C18 were between 0.003 and 0.025 mg/L at 48 h for 10 and 100 mg/L dose groups. - Details on test conditions:
- Intensity of irradiation: approx. 900 lux
Photoperiod: 16 h light/ 8 h darkness - Reference substance (positive control):
- no
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- ca. 40 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: Loading rates
- Basis for effect:
- mobility
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EL100
- Effect conc.:
- > 3 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: Loadin rates
- Basis for effect:
- mobility
- Details on results:
- Nominal test concentrations were 10, 30, 100, 1000, and 3000 mg/L. No solvent was used. Instead, the water accommodated fraction (WAF) was used in the test chambers. Measured concentrations in samples collected from the 10 and 100 mg/L chambers were less than 1% of nominal. The solubility of the lowest carbon chain length in this compound, C12, is 3 mg/L, therefore the EC50 was greater than the solubility limit.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Based on the results of the read across study, the 48 h EL50 of the test substance is considered to be 40 mg/L WAF (nominal).
- Executive summary:
A study was conducted to determine the acute toxicity of read across substance, Alcohols, C12-18 (purity not specified), to Daphnia magna, according to the EU Guideline 92/69/EWG, in compliance with GLP. Twenty test organisms were exposed to each nominal test substance concentrations of 0, 10, 30, 100, 1000, 3000 mg/L water accommodated fractions (WAF) for 48 h under static conditions. No solvent was used and instead, the water accommodated fraction (WAF) was used in the test chambers. The concentrations of test substance in the test vessels were measured using the fluid chromatography of dichloromethane extract. Measured concentrations in samples collected from the 10 and 100 mg/L chambers were less than 1% of nominal. The solubility of the lowest carbon chain length in this compound, C12, was 3 mg/L, therefore the EL50 was greater than the solubility limit. Immobilisation was recorded at 24 and 48 h and compared with control values. Based on the study results, the 48 h EL50 was calculated to be 40 mg/L WAF (nominal). As no immobility or other signs of stress were observed in the control and dissolved oxygen concentration remained at 99.3% mg/L, the test met all validity criteria. Under the study conditions, the 48 h EL50 was determined to be 40 mg/L (WAF; nominal) (OECD SIDS, 2006). Based on the results of the read across study, similar EL50 value can be considered for the test substance, 'mono- and di- C16 PSE, K+ and C16-OH and isostearyl isostearate'
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- 1999
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- significant methodological deficiencies
- Justification for type of information:
- Refer to section 13 of IUCLID for details on the read-across justification. The study with the read across substance is considered sufficient to fulfil the information requirements as further explained in the provided endpoint summary.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- other: German standard methods for the examination of water, waste water and sludge; bioassays (group L); determination of the effect of substances in water on microcrustaceans (Daphnia Shorttime Test) (L11).
- Deviations:
- not specified
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- not specified
- GLP compliance:
- not specified
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- not specified
- Limit test:
- no
- Total exposure duration:
- 48 h
- Reference substance (positive control):
- not specified
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 2.9 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- not specified
- Basis for effect:
- mobility
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- ca. 29 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- not specified
- Basis for effect:
- mobility
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Based on the results of the read across study, the 48 h EC50 for the test substance,was considered to be 2.9 mg/L.
- Executive summary:
A study was conducted to determine the acute toxicity of read across substance, 1-Decanol (purity not specified), to Daphnia magna, according to a method similar to OECD Guideline 202. Twenty daphnia magna were exposed to the range of test substance concentrations for 48 h, under static conditions. No analytical monitoring of the test substance was performed in the study. Immobilisation is recorded at 24 h and 48 h and compared with control values. The results were analysed in order to calculate the EC50 at 48 h. Under the study conditions, the 48 h EC50 and EC100 was determined to be 2.9 and 29 mg/L respectively (nominal) (OECD SIDS, 2006). Based on the results of the read across study, similar EC50 value can be considered for the test substance, 'mono- and di- C16 PSE, K+ and C16-OH and isostearyl isostearate'
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- 1998
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- KL2 due to RA
- Justification for type of information:
- Refer to section 13 of IUCLID for details on the read-across justification. The study with the read across substance is considered sufficient to fulfil the information requirements as further explained in the provided endpoint summary.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- yes
- Remarks:
- Only two replicates were used instead of four as recommended.
- Qualifier:
- according to guideline
- Guideline:
- ISO 6341 (Water quality - Determination of the Inhibition of the Mobility of Daphnia magna Straus (Cladocera, Crustacea))
- Deviations:
- yes
- Remarks:
- The pH of the dilution water was slightly higher (8.0 +/- 0.2).
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Remarks:
- Using the available analytical techniques, it was not possible to detect concentrations of the test substance in the test medium. Therefore, no chemical analysis was performed.
- Vehicle:
- no
- Details on test solutions:
- Preparation and application of test solutions
- Method: The test solutions were prepared separately and mixed with test medium for a defined period. Subsequently, the test solutions were allowed to stabilize in a separating funnel. The water phase in the middle of the separating funnel was used for testing and was identified as the Water Accommodated Fraction (WAF).
- Eluate: no
- Differential loading: yes
- Controls: yes, water control
- Evidence of undissolved material: All final test solutions were clear and colourless. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Test organism
- Common name: water flea
- Age at study initiation: < 24 h
- Method of breeding: Daphnia were held at a temperature of 18 – 22 °C. A new batch was started with newborn animals, i.e. less than 3 d old, by placing about 250 of them into 30 L of medium in an all-glass culture vessel. The maximum age of culture was 4 weeks. After 7 d of cultivation half of the medium was renewed. Daphnids were fed daily with a suspension of fresh water algae.
- Feeding during test: no - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Test temperature:
- 21.3 °C
- pH:
- 7.8 - 7.9
- Dissolved oxygen:
- 8.1 - 8.6 mg O2/L
- Nominal and measured concentrations:
- Nominal: 0, 86 mg/L (corresponding to 100 µL/L)
- Details on test conditions:
- Test system
- Test vessel: all-glass vessels
- Material, size, fill volume, headspace: all-glass, 100 mL, Fill volume: 80 mL, Headspace: 20 mL
- Aeration: no
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 2
Test medium/Water parameter
- Source/preparation of dilution water: Medium was prepared according to ISO guideline in milli-RO water
- Culture medium different from test medium: no
Other test condition
- Photoperiod: 16 h light / 8 h dark
Effects parameters measured
Immobility was recorded after 24 and 48 h.
Test concentrations
- Range finding study
- Test concentrations: control, WAFs at 10 and 100 mg/L (range finding study 1); control, WAFs at 0.86 and 8.6 mg/L (range finding study 2)
- Results used to determine the conditions for the definitive study: At WAFs prepared at 10 and 100 mg/L daphnids trapped at the surface of test solutions. At WAFs prepared at 0.86 and 8.6 mg/L the stabilisation period was increased to 24 h to overcome daphnids becoming trapped at the surface. No effects were observed in the second range-finding study. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 86 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: Water Accommodated Fraction (WAF)
- Basis for effect:
- mobility
- Details on results:
- - Mortality of control: no
- Effect concentrations exceeding solubility of substance in test medium: The test solutions at 86 mg/L (nominal) exceeded the maximum water solubility of the test substance. - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- EC50/LC50: 48 h EC50 was 0.5 mg/L (95% Confidence Limit: 0.4 - 0.6 mg/L) - Validity criteria fulfilled:
- yes
- Conclusions:
- Based on the results of read across study, the 48 h EL50 of the test substance, 'mono- and di- C16 PSE, K+ and C16-OH and isostearyl isostearate' for Daphnia magna was determined to be >86 mg/L (nominal) WAF.
- Executive summary:
A study was conducted to determine the acute toxicity of read across substance, octyldodecyl isooctadecanoate (purity: assumed to be 100%), to Daphnia magna, according to OECD Guideline 202 and EU Method C.2, in compliance with GLP. Twenty test organisms each were exposed to nominal concentration of 86 mg/L (i.e., corresponding to 100 µL/L) for 48 h under static conditions. Potassium dichromate was used as positive control substance. Using the available analytical techniques, it was not possible to detect concentrations of the read across substance in the test medium. Therefore, no chemical analysis was performed. The test solutions at 86 mg/L (nominal) exceeded the maximum water solubility of the test substance, therefore concentration identified as Water Accommodated Fraction (WAF) was considered for reporting the result. Immobilisation was recorded at 24 and 48 h and compared with control values. Based on immobility compared to the control, the 48 h EL50 was determined to be >86 mg/L (nominal) WAF. No other symptoms of toxicity were observed. Positive control substance results were considered valid. As no immobility or other signs of stress were observed in the control and dissolved oxygen concentration remained at ≥3 mg/L, this test had satisfied all the validity criteria. Under the study conditions, the 48 h EL50 of the read across substance for Daphnia magna was determined to be >86 mg/L (nominal) WAF (Notox, 1998). Based on the results of read across study, similar EL50 value can be expected for the test substance, 'mono- and di- C16 PSE, K+ and C16 -OH and isostearyl isostearate'.
Referenceopen allclose all
Table 1: Analytical results
Nominal concentration of test substance (mg/L) |
Measured concentration of test substance (mg/L) |
Mean measured concentration (mg/L) |
Mean measured concentration (%) |
|||
0 h |
48 h |
|||||
(mg/L) |
% of nominal |
(mg/L) |
% of nominal |
|||
Control |
<LOQ |
- |
<LOQ |
- |
0 |
- |
0.625 |
<LOQ |
- |
<LOQ |
- |
0 |
0 |
1.25 |
<LOQa |
- |
<LOQb |
- |
0 |
0 |
2.5 |
<LOQ |
- |
<LOQ |
- |
0 |
0 |
5 |
0.43 |
9 |
<LOQ |
- |
0.21 |
4 |
10 |
0.68 |
7 |
<LOQ |
- |
0.34 |
3 |
All analytical measurements quoted to 2 significant figures. Arithmetic means are used due to the zero values present.
a Mean of triplicate analyses: <LOQ, <LOQ, <LOQ mg/L.
b Mean of triplicate analyses: <LOQ, <LOQ, <LOQ mg/L.
The limit of quantification (LOQ) in this study was 0.4 mg/L for all test solutions. The instrument LOQ was 0.2 mg/L but during analysis, samples from the control and each test concentration were diluted ×2, doubling the LOQ. Values in Table 1 have been corrected for these dilutions.
Table 2: Daphnia magna response
Time (h) |
Nominal concentration of test substance (mg/L) |
Mean measured concentration of test substance (mg/L) |
Number immobilised per replicate |
Total number tested |
Total number immobilised |
Percentage immobilised |
|
||||
A |
B |
C |
D |
|
|||||||
24 |
Control |
0 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
|
0.625 |
0 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
||
1.25 |
0 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
||
2.5 |
0 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
|
|
5 |
0.21 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
|
|
10 |
0.34 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
|
|
48 |
Control |
0 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
|
0.625 |
0 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
||
1.25 |
0 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
||
2.5 |
0 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
||
5 |
0.21 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
||
10 |
0.34 |
0 |
0 |
0 |
0 |
20 |
0 |
0 |
|
Validity criteria
As no immobility or other signs of stress were observed in the control and dissolved oxygen concentration remained at ≥3 mg/L, this test has satisfied all OECD Guideline 202 validity criteria.
Description of key information
Based on the available weight of evidence from studies for substances representative of the main constituents, the 48 h EC50 of the test substance, 'mono- and di- C16 PSE, K+ and C16-OH and isostearyl isostearate' for toxicity to Daphnia magna is considered to be >0.34 mg/L (measured).
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.34 mg/L
Additional information
In absence of short-term toxicity to aquatic invertebrates with the test substance, the endpoint has been assessed based on studies for substances representative of the main constituents, which can be categorised as phosphate esters (PSE i.e., mono- and di C16 PSE, K+), alcohol (i.e., hexadecanol) and isoalkylester (i.e., isostearyl isostearate). The results are presented below:
Constituent: PSE - read across study:
A study was conducted to determine the acute toxicity of read across substance, mono- and di- C16 PSE, K+ and H3PO4 (100%), to Daphnia magna, according to the OECD Guideline 202, in compliance with GLP. Twenty test organisms were exposed to each nominal read across substance concentrations of 0, 0.625, 1.25, 2.5, 5 and 10 mg/L for 48 h under static conditions. The concentrations of read across substance in the test vessels were measured using the high-performance liquid chromatography method. The mean measured concentrations of read across substance were determined to be 0, 0, 0, 0, 0.21 and 0.34 mg/L. Immobilisation was recorded at 24 and 48 h and compared with control values. Based on immobility compared to the control (p <0.05), the 48 h NOEC was determined to be 0.34 mg/L (measured) and the LOEC was >0.34 mg/L (measured). No other symptoms of toxicity were observed. Based on the study results, the 48 h EC50 was calculated to be >0.34 mg/L (measured). As no immobility or other signs of stress were observed in the control and dissolved oxygen concentration remained at ≥3 mg/L, this test has satisfied all validity criteria. Under the study conditions, the 48 h EC50 of the read across substance for Daphnia magna was determined to be >0.34 mg/L(measured) (Scymaris, 2018).
Constituent: alcohol - read across studies:
Study 1: A study was conducted to determine the acute toxicity of read across substance, Alcohols, C12-18 (purity not specified), to Daphnia magna, according to the EU Guideline 92/69/EWG, in compliance with GLP. Twenty test organisms were exposed to each nominal test substance concentrations of 0, 10, 30, 100, 1000, 3000 mg/L water accommodated fractions (WAF) for 48 h under static conditions. No solvent was used and instead, the water accommodated fraction (WAF) was used in the test chambers. The concentrations of test substance in the test vessels were measured using the fluid chromatography of dichloromethane extract. Measured concentrations in samples collected from the 10 and 100 mg/L chambers were less than 1% of nominal. The solubility of the lowest carbon chain length in this compound, C12, was 3 mg/L, therefore the EL50 was greater than the solubility limit. Immobilisation was recorded at 24 and 48 h and compared with control values. Based on the study results, the 48 h EL50 was calculated to be 40 mg/L WAF (nominal). As no immobility or other signs of stress were observed in the control and dissolved oxygen concentration remained at 99.3% mg/L, the test met all validity criteria. Under the study conditions, the 48 h EL50 was determined to be 40 mg/L (WAF; nominal) (OECD SIDS, 2006).
Study 2: A study was conducted to determine the acute toxicity of read across substance, 1-Decanol (purity not specified), to Daphnia magna, according to a method similar to OECD Guideline 202. Twenty daphnia magna were exposed to the range of test substance concentrations for 48 h, under static conditions. No analytical monitoring of the test substance was performed in the study. Immobilisation is recorded at 24 h and 48 h and compared with control values. The results were analysed in order to calculate the EC50 at 48 h. Under the study conditions, the 48 h EC50 and EC100 was determined to be 2.9 and 29 mg/L respectively (nominal) (OECD SIDS, 2006).
Constituent isoalkylester - read across study:
A study was conducted to determine the acute toxicity of read across substance, octyldodecyl isooctadecanoate (purity: assumed to be 100%), to Daphnia magna, according to OECD Guideline 202 and EU Method C.2, in compliance with GLP. Twenty test organisms each were exposed to nominal concentration of 86 mg/L (i.e., corresponding to 100 µL/L) for 48 h under static conditions. Potassium dichromate was used as positive control substance. Using the available analytical techniques, it was not possible to detect concentrations of the read across substance in the test medium. Therefore, no chemical analysis was performed. The test solutions at 86 mg/L (nominal) exceeded the maximum water solubility of the test substance, therefore concentration identified as Water Accommodated Fraction (WAF) was considered for reporting the result. Immobilisation was recorded at 24 and 48 h and compared with control values. Based on immobility compared to the control, the 48 h EL50 was determined to be >86 mg/L (nominal) WAF. No other symptoms of toxicity were observed. Positive control substance results were considered valid. As no immobility or other signs of stress were observed in the control and dissolved oxygen concentration remained at ≥3 mg/L, this test had satisfied all the validity criteria. Under the study conditions, the 48 h EL50 of the read across substance for Daphnia magna was determined to be >86 mg/L (nominal) WAF (Notox, 1998).
Overall, based on the available weight of evidence information from studies for substances representative of the main constituents, similar absence of toxicity up to highest soluble test concentrations can be expected for the test substance, 'mono- and di- C16 PSE, K+ and C16-OH and isostearyl isostearate'. As a conservative approach, the lowest 48 h EC50 value, which was established as >0.34 mg/L (mean measured) has been considered further for hazard/risk assessment.
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