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EC number: 208-736-6 | CAS number: 540-10-3
- 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:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- Refer to analogue justification provided in IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 21 d
- Dose descriptor:
- NOELR
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- reproduction
- Remarks on result:
- other:
- Remarks:
- Source: CAS 36078-10-1, Dako, 2013, D. magna, 21 d
- Duration:
- 21 d
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- reproduction
- Remarks on result:
- other:
- Remarks:
- Source: CAS 36078-10-1, Dako, 2013, D. magna, 21 d
- Duration:
- 21 d
- Dose descriptor:
- NOELR
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- reproduction
- Remarks on result:
- other:
- Remarks:
- Source: CAS 3687-45-4, Ecogreen, 2013, D. magna, 21 d
- Duration:
- 21 d
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- mortality
- Remarks on result:
- other:
- Remarks:
- Source: CAS 3687-45-4, Ecogreen, 2013, D. magna, 21 d
- Conclusions:
- No effects on the reproduction of D. magna (OECD 211) up to the limit of water solubility (< 0.05 mg/L).
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 02 Aug - 11 Dec 2012
- 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:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- LUBW Landesanstalt für Umwelt, Messungen und Naturschutz, Baden-Württemberg, Germany
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: Control, 6.75, 25 and 100 mg/L
- Sampling method: At the start (0 h), at the end (21 d) and at least once a week, 3.8 mL sample were taken from the test vessels A, C and E (100, 25 and 6.75 mg/L) and the control vessels at the beginning and at the end of a medium-change interval or chemical analysis.
- Sample storage conditions before analysis: Sample storage in 4 mL brown glass vials (filled up to the brim to avoid oxidative processes), maximum storage period of 8 d at 5 °C ± 3 °C before analysis. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Due to the low water solubility of the test item, the study was performed with the water accommodated fraction (WAF) prepared with M4 medium according to OECD 202. The suspension was stirred for 24 hours at 20 – 22 °C in diffuse light. After stirring was stopped, the suspension was allowed to float and sediment for a period of 1 hour. After sedimentation and floatation period the WAF was clear and no particles could be observed. The test solution was taken from the middle of the suspension on the beaker using a glass tube and transferred into the test vessels. About 75 mL test solution was transferred into each test vessel (100 mL glass beakers). WAFs were prepared 3 x week.
- Controls: yes, M4 medium - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Strain/clone: Straus
- Source: German Federal Environmental Agency, department V 3.2, Berlin, Germany
- Age of parental stock: 0.5 – 21.5 h
- Feeding during test
- Food type: Suspension of the algae Desmodemus subspicatus
- Amount: 0 to 6 days: 0.1 mg C/Daphnia/day, 7 – 21 days: 0.2 mg C/Daphnia/day
- Frequency: daily
ACCLIMATION
- Acclimation conditions (same as test or not): The Daphnia are held at 20 ± 2 °C with a light : dark cycle of 16 : 8 h.
- Type and amount of food: Suspension of the algae Desmodesmus subspicatus, 0.1 mg C/Daphnia/days
- Feeding frequency: Fed during working days. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 21 d
- Test temperature:
- 20.6 - 21.8 °C
- pH:
- 7.6 - 8.2
- Dissolved oxygen:
- 7.7 - 8.5 mg O2/L
- Nominal and measured concentrations:
- Nominal: control, 6.75, 12.5, 25, 50, 100 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL beakers
- Type (delete if not applicable): covered with a transparent plastic foil
- Material, size, headspace, fill volume: glass, 100 mL, headspace: 25 mL, fill volume: 75 mL
- Renewal rate of test solution (frequency/flow rate): three times per week
- No. of organisms per vessel: 1
- No. of vessels per concentration (replicates): 10
- No. of vessels per control (replicates): 10
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Elendt-M4-medium, according to OECD 202. Before the addition of the M4 stock solutions the water was aerated for 2 hours to allow the dissolved oxygen concentration to reach its saturation.
- Intervals of water quality measurement: With every medium renewal the pH and oxygen content were measured.
OTHER TEST CONDITIONS
- Adjustment of pH:
- Photoperiod: 16 h light : 8 h dark
- Light intensity: 6.73 µmol/m2
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): Immobility and reproduction (cumulative offspring was recorded daily. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 21 d
- Dose descriptor:
- NOELR
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- reproduction
- Details on results:
- - Mortality of parent animals: Only in one vessel (B: 50 mg/L) one dead Daphnia was found among the parent animals. This animal died because of an accident during the medium change and not because of influence of the test item.
- Body length and weight of parent animals: Control: mean 4.282 ± 0.152 mm; 6.8 mg/L: mean 4.285 ± 0.120 mm; 12.5 mg/L: mean 4.211 ± 0.146 mm; 25 mg/L: mean 4.284 ± 0.139 mm; 50 mg/L: mean 4.373 ± 0.122 mm; 100 mg/L: mean 4.278 ± 0.114 mm
- Time to first brood release or time to hatch: Control: mean 8.50 ± 0.00 day; 6.8 mg/L: mean 9.20 ± 1.16 day; 12.5 mg/L: mean 9.20 ± 0.82 day; 25 mg/L: mean 9.70 ± 1.14 day; 50 mg/L: mean 9.60 ± 2.62 day; 100 mg/L: mean 9.20 ± 1.64 day - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- Relevant effect levels: EC50 (24 h): 1.92 mg/L; EC50 (48 h): 1.50 mg/L - Reported statistics and error estimates:
- Williams Multiple t-test procedure using ToxRat v2.09 (ToxRat solutions, Alsdorf, Germany)
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 05 Jan - 22 May 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 211 (Daphnia magna Reproduction Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.20 (Daphnia magna Reproduction Test)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Swiss Federal Office of Public Health, Bern, Switzerland
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: Control, 100 mg/L
- Sampling method: Duplicate samples were taken from the freshly prepared test medium of the single test concentration and from the control at one treatment period of the first, second and last week of the test (day 0, 2, 7 and 16, respectively). To determine the maintenance of the test substance concentration in test medium, stability samples were taken at the end of two test medium renewal periods of 48 h (day 2 and 9) and at the end of two renewal periods of 72 h (days 5 and 19).
- Sample storage conditions before analysis: All samples were stored deep-frozen (at about -20 °C) and protected from light immediately after sampling. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: A dispersion with the nominal concentration of 100 mg/L was prepared prior to the start of the test and prior to each medium renewal by dispersing 400 and 200 mg of the test item (dosed in the range of 400 to 401 mg on days 0, 7 and 16 and in the range of 200 to 201 mg on days 2, 5, 9, 12, 14 and 19) in 4000 and 2000 mL of test water under intense stirring for 96 h at room temperature in the dark to avoid photolytic degradation. After the 96 h stirring period, the test item was filtered through a membrane filter (Schleicher & Schuell, Type NC45, pore size 0.45 µm). The test medium was prepared just before the start of the test (= addition of daphnids) and before each test medium renewal.
- Eluate: no
- Differential loading: no
- Controls: yes, test medium control - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Source: Originally supplied by the University of Sheffield/UK in 1992. Since this date, the clone is successfully bred at Harlan Laboratories.
- Age of parental stock (mean and range, SD): < 24 h
- Feeding during test
- Food type: food mixture containing a suspension of green algae of the species Scenedesmus subspicatus (freshly grown at the laboratory) and a fish food suspension. The fish food suspension was prepared by dispersing 10 g of powdered commercial fish diet (TETRA MIN Hauptfutter, obtained from TETRA-Werke, Melle, Germany) in 500 mL of test water. The suspension was allowed to stand for 4 hours. Then, 400 mL of the supernatant were taken, diluted 1:1 with test water and boiled. The suspension was stored deep frozen in small quantities until use.
- Amount: 0.20 mg TOC per Daphnia and day
- Frequency: daily
- Method of breeding: Each stock animal was maintained separately in a 100 mL glass beaker filled with about 80 mL culture medium and was transferred twice a week to fresh medium. The condition of the stock animals was frequently checked. No signs of stress were observed and the brood stock was healthy.
ACCLIMATION
- Acclimation period: The daphnids used for the test originated form parental daphnids that were at least 14 d old but not older than four weeks and were not first brood progeny.
- Acclimation conditions (same as test or not): same as test
- Type and amount of food: same as test
- Feeding frequency: three times a week - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 21 d
- Test temperature:
- 20 - 21 °C
- pH:
- 7.7 - 8.1
- Dissolved oxygen:
- 8.2 - 9.2 mg O2/L
- Nominal and measured concentrations:
- nominal: control, 100 mg/L
measured: < LOQ in the control and treatment - Details on test conditions:
- TEST SYSTEM
- Test vessel: beakers
- Type (delete if not applicable): covered with glass plates to reduce loss of water by evaporation and to avoid the entry of dust into the solutions.
- Material, size, headspace, fill volume: glass, 100 mL, headspace: 20 mL, fill volume: 80 mL
- Aeration: no
- Renewal rate of test solution (frequency/flow rate): renewed on days 2, 5, 7, 9, 12, 14, 16 and 19.
- No. of organisms per vessel: 1
- No. of vessels per concentration (replicates): 20
- No. of vessels per control (replicates): 20
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water (Elendt M7 medium)
- Alkalinity: 0.9 mmol/L
- Water hardness: 250 mg/L as CaCO3
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 h light / 8 h dark (30 min transition period)
- Light intensity: 400 - 540 lux
EFFECT PARAMETERS MEASURED: Mortality and reproduction on days 0-2 and thereafter at least three times per week before renewal of test media. On the same dates, the test repliacates were observed for the number of living and dead offspring and for the presence of aborted eggs. - Reference substance (positive control):
- no
- Duration:
- 21 d
- Dose descriptor:
- NOELR
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- WAF
- Basis for effect:
- mortality
- Details on results:
- - Mortality of parent animals: 0% in control; 5% in treatment
- Type and number of behavioural abnormalities: No visible abnormalities were observed during the test.
- No. of offspring produced after 21 d per female: 142 (mean, control); 137 (mean, treatment)
- Time to first brood release or time to hatch: day 9 in control and treatment - Reported statistics and error estimates:
- Student t-test (one-sided smaller, α = 0.05) with the mean values of living offspring.
Referenceopen allclose all
Table 1: Effective Concentrations for Mean Cumulative Offspring per parent animal
Concentration [mg/L] |
Mean offspring |
Standard deviation |
n |
% Reduction |
Control |
99.0 |
6.80 |
10 |
0.0 |
6.8 |
97.0 |
8.80 |
10 |
2.3 |
12.5 |
102.0 |
6.10 |
10 |
-3.1 |
25.0 |
103.0 |
10.60 |
10 |
-4.6 |
50.0 |
97.0 |
37.60 |
9 |
1.9 |
100.0 |
108.0 |
10.40 |
10 |
-9.5 |
The analytical determination of the test substance concentration indicated that in almost all vessels no test substance concentration could be measured up to the limit of quantification (LLOQ) of 5 µg/L reflecting the very low water solubility of the test substance. Only in three test samples the test substance could be detected with a recovery rate of ≤ 4.4%.
Description of key information
No chronic effects up to the limit of water solubility (OECD 211, D. magna); read-across
Key value for chemical safety assessment
Additional information
There is no study available assessing the long-term toxicity of the target substance hexadecyl palmitate (CAS 540-10-3) to aquatic invertebrates. Therefore, a read-across to the two structurally related source substances (Z)-octadec-9-enyl oleate (CAS 3687-45-4) and dodecyl oleate (CAS 36078-10-1) was conducted in accordance with Regulation (EC) No 1907/2006 Annex XI, 1.5. Both source substances are characterized by similar fatty acid and fatty alcohol chain lengths as the target substance. The target substance is the reaction product of a C16 fatty acid and alcohol. The source substance (Z)-octadec-9-enyl oleate (CAS 3687-45-4) consists of a C18:1 fatty acid and a C18:1 fatty alcohol. The source substance dodecyl oleate (CAS 36078-10-1) is an ester of a C18 fatty acid and a C12 fatty alcohol. Thus, the two source substances are considered suitable representatives for the assessment of the long-term toxicity of the target substance to aquatic invertebrates. A detailed read-across justification is provided in in the analogue justification in IUCLID section 13.
Both available studies were conducted according to OECD guideline 211 and GLP.
In the study with the source substance (Z)-octadec-9-enyl oleate (CAS 3687-45-4), a limit test with a water accommodated fraction (WAF) with a nominal loading rate of 100 mg/L was performed with D. magna due to the very low water solubility (< 0.05 mg/L) of the test item (Ecogreen, 2013). The chemical analysis resulted in concentrations below the analytical detection limit of 0.0423 mg/L, reflecting the very low water solubility of the test item. No effects on reproduction and mortality were recorded after 21 d resulting in a NOELR (21 d) of ≥ 100 mg/L. 0% mortality was recorded in the control whereas 5% mortality was observed in the treatment. This level of mortality is regarded as natural and is tolerated by the test guideline.
In the study with the source substance dodecyl oleate (CAS 36078-10-1), D. magna was exposed to five WAFs with nominal concentrations ranging from 6.75 to 100 mg/L in a semi-static test for 21 d (Dako, 2013). Chemical analysis resulted in concentrations below the analytical detection limit of 0.005 mg/L, reflecting the very low water solubility of the test item. After 21 d, no effects on the reproduction of D. magna were observed and a NOELR (21 d) of ≥ 100 mg/L (nominal) was derived. One dead animal was recorded at 50 mg/L but it was not attributed to any substance specific effect (accident during medium change).
Based on the structural and chemical similarity of the target and source substances, the target substance is expected to exhibit a similar ecotoxicological profile as the source substances. Therefore, it can be concluded that hexadecyl palmitate (CAS 540-10-3) will not exhibit long-term effects on aquatic invertebrates up to the limit of water solubility (< 0.846 µg/L).
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