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EC number: 944-520-4 | 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:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: read-across from reliable QSAR (ECOSAR) data
- Justification for type of information:
- The read across justification is presented in the Endpoint Aquatic toxicity because for algae the same substance is used and the reasoning is included in one document. The accompanying files are also attached there.
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.119 mg/L
- Basis for effect:
- mobility
- Remarks on result:
- other: read-across from Longifoloene Coeur
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.33 mg/L
- Basis for effect:
- mobility
- Remarks on result:
- other: read-across from Cedryl acetate 'mono'
- Validity criteria fulfilled:
- yes
- Remarks:
- Reliable and adequate documentation is present for the read across rationale.
- Conclusions:
- The EC50 of Daphnia for Cedryl Acetate EOA is 0.12 mg/l based on read across from Longifolene Coeur.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 17 April 2016 - 21 July 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- This information is used for read across to Cedryl Acetate EOA
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Guidance document on aquatic toxicity testing of difficult items and mixtures, OECD series on testing and assessment number 23, December 14, 2000
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: all test concentrations and the control
- Sampling method:
Frequency: At the start and the end of both 24-hour renewal periods
Volume: 4.0 mL from the approximate centre of the test vessels
- Sample storage conditions before analysis: Not applicable, samples were analysed on the day of sampling
At the end of each renewal period, samples were taken from one replicate of each test concentration and the control. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: water accommodated fraction (WAF)
The batch of Cedryl Acetate tested was a clear pale yellow to yellow liquid with a purity of 53.6% and the test item was not completely soluble in test medium at the loading rates initially prepared. No correction was made for the purity/composition of the test item.
All test concentrations were prepared separately. Loading rates ranging from 1.0 to 100 mg/L were magnetically stirred in closed vessels for two days to reach the maximum solubility of the test item in the test medium. The resulting aqueous mixtures were left to stabilize for 1-1½ hours whereafter the WAF was siphoned out through glass wool and used for testing.
The final test solutions were all clear and colourless. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna (Straus, 1820)
- Source: In-house laboratory culture with a known history, at least third generation, obtained by acyclical parthenogenesis under specified breeding conditions. Daphnids originated from a healthy stock, 2nd to 5th brood, showing no signs of stress such as mortality >20%, presence of males, ephippia or discoloured animals and there was no delay in the production of the first brood.
- Age at study initiation: young daphnids with an age of < 24 hours, from parental daphnids of more than two weeks old.
- Method of breeding: start of each batch with newborn daphnids, i.e. less than 3 days old, by placing about 250 of them into 5 litres of medium (M7) in an all-glass culture vessel. Renewal of the cultures: after 7 days of cultivation half of the medium twice a week.
- Validity of batch: Daphnids originated from a healthy stock, 2nd to 5th brood, showing no signs of stress such as mortality >20%, presence of males, ephippia or discoloured animals and there was no delay in the production of the first brood.
- Feeding during test: no
ACCLIMATION
- Acclimation period: no - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- no
- Hardness:
- 180 mg CaCO3/L
- Test temperature:
- 20-21°C
- pH:
- 7.6-7.9
- Dissolved oxygen:
- in fresh solutions (t=0, t=24): 8.4-9.0 mg O2/L
in used solutions (t=24, t=48): 8.1-8.5 mg O2/L - Nominal and measured concentrations:
- Based on the results of the combined limit/range-finding test, the EC50 was expected to be in the range of a WAF prepared at loading rates of 10 mg/L, thus the following test concentrations were assigned to the definitive test:
Final test 2 - WAFs prepared separately at loading rates of 2.2, 4.6, 10, 22 and 46 mg/L
Final test 2 - mean measured concentrations: 0.2, 0.35, 0.63, 1.4 and 1.7 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: 60 mL, all-glass, air-tight closed; fill-volume: 60 mL
- Aeration: None
- Renewal rate of test solution: every 24 hours
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Adjusted ISO medium
- Culture medium different from test medium: Yes, M7
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 h daily
EFFECT PARAMETERS MEASURED: mobility at 24 and 48 hours ; pH and dissolved oxygen at the start and the end of both renewal periods, for all concentrations and the control. Temperature continuously.
RANGE-FINDING STUDY
- Test concentrations: WAFs prepared separately at loading rates of 1.0, 10 and 100 mg/L
- Results used to determine the conditions for the definitive study: yes - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate (July 2016)
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.33 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CI: 0.20 - 0.63 mg/L
- Details on results:
- Recovery: In final test 2, measured concentrations at the end of the renewal periods ranged from 69-111% relative to initial analysed concentrations, except for the 4.6 mg/L and 22 mg/L concentrations prepared for the second renewal period, where the concentrations were above and much below, relative to the initial analysed concentrations (129 and 26%, respectively). (see table 3 below)
Individual pH, temperature and dissolved oxygen values remained within acceptable limits throughout the duration of the study. - Results with reference substance (positive control):
- The 48h-EC50 was within the expected range of 0.30 to 1.0 mg/L, to be specific between 0.32 and 0.56 mg/L. 100% effect was observed at 1.0 mg/L.
- Validity criteria fulfilled:
- yes
- Remarks:
- (1) In the control, no daphnids became immobilised or showed other signs of disease or stress. (2) The oxygen concentration at the end of the test was ≥3 mg/L in control and test vessels.
- Conclusions:
- The 48h-EC50 value determined for Daphnia magna was 0.33 mg/L based on mean (measured) concentrations.
- Executive summary:
A study was performed to assess the acute toxicity of the substance to Daphnia magna. The study was conducted in accordance with OECD Guideline for Testing of Chemicals No. 202 under semi-static conditions. Based on the results of a combined limit/range-finding test, the following nominal concentrations were tested in the definitive test: WAFs prepared separately at loading rates of 2.2, 4.6, 10, 22 and 46 mg/L. For each concentration and a control group, twenty Daphnia magna (less than 24 hours old) were exposed for 48 hours in air-tight closed vessels. The incidence of immobilisation was recorded for each test and control group at 24 hours and at 48 hours. Samples taken from all concentrations at the start and the end of both 24-hour renewal periods were analysed with a validated GC-FID method.
Measured concentrations at the end of the renewal periods ranged from 69-111% relative to initial analysed concentrations, except for the 4.6 mg/L and 22 mg/L concentrations prepared for the second renewal period, where the concentrations were above and much below, relative to the initial analysed concentrations (129 and 26%, respectively). Based on these results, the mean measured concentrations were calculated. The range tested based on mean concentrations was 0.2, 0.35, 0.63, 1.4 and 1.7 mg/L.
The 48h-EC50 value determined for Daphnia magna was 0.33 mg/L based on mean measured concentrations.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 09 January 2017 - 25 January 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- This information is used for read across to Cedryl Acetate EOA
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: OECD Series on Testing and Assessment, No. 23, "Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures"
- Version / remarks:
- December 15, 2000
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: control and all test concentrations
- Sampling method: 20 mL were taken from the freshly prepared test media of all test concentrations and the control at the start of the test, and the test medium renewal at Day 1; 20 mL were collected from pooled test media of all test concentrations and the control at the end of the first renewal period at Day 1, and at the end of the test (t=48 h)
- Sample storage conditions before analysis: All samples were extracted stand-by with hexane and the extracts were stored in a refrigerator at 4°C ± 4°C until analysis. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: preparation of a saturated solution (direct addtion to test medium) - Due to the low limit of water solubility and oily characteristic of the test item a water accommodated fraction (WAF) was prepared. Additionally, the test item is highly volatile. Therefore a supersaturated stock solution of only the highest concentration (330 mg/L) was prepared to dissolve as much substance as possible. The stock solution was stirred gently for 24 hours. Vessels with a conical glass stopper were used and the head space was reduced to a minimum to minimise volatility. After the stirring period, the stock solution was allowed to rest for 1 hour until phase separation. Then, the test medium was extracted from below the water surface and used as the highest test concentration. The lower concentrations were prepared by diluting the highest concentration with adequate volumes of test water to reduce loss due to volatilisation. The test media were prepared just before introduction of the daphnids (= start of the test) and test medium renewal on Day 1.
- Controls: test medium without test substance
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): yes, in the freshly prepared highest test concentration (= 100% saturated solution) some test item was floating at the water surface as small droplets - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna (Straus)
- Strain/clone: clone 5
- Source: test facility's in-house laboratory culture
- Feeding during culture:
* Food type: green algae (Desmodesmus subspicatus)
* Frequency: daily
- Feeding during test: no
- Age at study initiation: young daphnids with an age of < 24 hours
ACCLIMATION
- Acclimation period: not necessary, since the test was performed in the same medium as the culturing
METHOD FOR PREPARATION AND COLLECTION OF EARLY INSTARS OR OTHER LIFE STAGES:
The daphnids were bred in the laboratories of ibacon under similar temperature and light conditions as used in the test. The cultivation of the parental daphnids was performed in Elendt M4 medium. The test organisms were not first brood progeny. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- no
- Hardness:
- 250 mg/L (as CaCO3)
- Test temperature:
- 19.3-20.0°C
- pH:
- fresh solutions: 8.0-8.1
used solutions: 8.0 - Dissolved oxygen:
- fresh solutions: 8.7-9.0 mg O2/L
used solutions: 8.3-8.8 mg O2/L - Conductivity:
- < 5 μScm^-1
- Nominal and measured concentrations:
- Due to the low limit of water solubility and volatility a water accommodated fraction (WAF) was prepared with a nominal loading rate of 300 mg test item/L as highest test concentration. Dilutions of the highest concentrations of 1:2, 1:4, 1:8 and 1:16 and a control were tested.
The WAF and its dilutions are corresponding to the following geometric mean measured concentrations of the test item:
0.141, 0.059, 0.029, 0.014 and 0.008 mg test item/L
Effect parameters are beased on geometric mean measured concentrations since the test item concentrations were not within ± 20% of the measured initial concentrations during the test. Additionally, preparation of fresh test solutions proved not reproducible (at renewal only 57.6-69.2% of the concentrations measured at t=0 were achieved; calculated by the reviewer). - Details on test conditions:
- TEST SYSTEM
- Test vessel: Glass beakers of approximately 110 mL volume containing as much test medium as possible (i.e. the remaining head space was reduced to a technical possible minimum of some mL), kept closed during the whole period of the study with a conical glass stopper to avoid loss of the test item due to volatilisation.
- Aeration: no
- Renewal rate of test solution (frequency): 1 renewal after 24 hours
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Elendt M4 according to OECD202
- Alkalinity: 0.9 mmol
- Culture medium different from test medium: no
- Intervals of water quality measurement: temperature, pH-values and dissolved oxygen concentrations were determined in all freshly prepared and aged test media of each treatment group
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 h light : 8 h dark
- Light intensity: 440 to 720 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : mobility (at 24 and 48 hours)
RANGE-FINDING STUDY
- Test concentrations: not specified in the report
- Results used to determine the conditions for the definitive study: yes - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate (September 2016)
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.119 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% C.I. 0.086-0.216 mg/L
- Details on results:
- - Behavioural abnormalities: no
- Mortality of control: no
- Other adverse effects control: no
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: no
- Effect concentrations exceeding solubility of substance in test medium: no
- Other:
* Relative to initial [%] (based on the mean of measured conc.) ranged from 29.4 - 48.5% in the first renewal period and 27.5-55.9% in the second renewal period (calculated by the reviewer) - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- Dose-response test: yes; tested concnetrations: 0.125, 0.25, 0.5, 1.0 and 2.0 mg/L
- ECx: 24h-EC50 = 0.959 mg/L (no 95% C.I. determinable); 48h-EC50 = 0.765 (95% C.I. 0.650-0.888 mg/L)
- Other: the sensitivity of the daphnids was consistent with the level proposed by the OECD 202 guideline (i.e. 24h-EC50 between 0.6 and 2.1 mg potassium dichromate/L) - Reported statistics and error estimates:
- The EC50 and EC10 and the 95 % confidence limits were calculated by probit analysis.
The NOEC was determined directly from the raw data.
The software used to perform the statistical analysis was ToxRat Professional, Version 3.2.1, ToxRat Solutions GmbH. - Validity criteria fulfilled:
- yes
- Remarks:
- 1) In the control, no daphnids became immobilised or showed other signs of disease or stress. 2) The oxygen concentration at the end of the test was ≥3 mg/L in control and test vessels.
- Conclusions:
- The 48h-EC50 value to Daphnia magna was 0.119 mg/L based on geometric mean measured concentrations.
- Executive summary:
A study was performed to assess the acute toxicity of the substance to Daphnia magna. The study was conducted in accordance with OECD Guideline for Testing of Chemicals No. 202 and GLP under semi-static conditions. Based on the results of a range-finding test, the following nominal concentrations were tested in the definitive test: untreated control, a water accommodated fraction (WAF) prepared at a nominal loading rate of 300 mg test item/L as highest test concentration and dilutions of the highest concentrations of 1:2, 1:4, 1:8 and 1:16. For each concentration and a control group, twenty Daphnia magna (less than 24 hours old) were exposed for 48 hours in air-tight closed vessels. The incidence of immobilisation was recorded for each test and control group at 24 hours and at 48 hours. Samples taken from all concentrations at the start and the end of both 24 -hour renewal periods were analysed with a validated GC-FID method.
Measured concentrations in used test solutions ranged from 29 -49% of initial in the first renewal period, and from 26 -58% of initial in the second renewal period. Since test concentrations did not remain stable during the 24 -hour renewal periods (i.e. not within 80 -120% of initial), geometric mean measured concentrations were calculated. The range tested based on geometric mean measured concentrations was 0.141, 0.059, 0.029, 0.014 and 0.008 mg test item/L. The 48h-EC50 value to Daphnia magna was 0.119 mg/L based on geometric mean measured concentrations.
Referenceopen allclose all
A range-finding test and two final test were performed.
Final test 1 was rejected because analytical results were not acceptable at 48 hours, thus only data from Final test 2 (same test set-up as Final test 1) are presented.
Table 1: Number of introduced daphnids and incidence of immobility in Final test 2
Time (h) |
Replicate |
Cedryl Acetate, WAF at x mg/L |
|||||
Control (-) |
2.2 (0.20) |
4.6 (0.35) |
10 (0.63) |
22 (1.4) |
46 (1.7) |
||
0 |
A |
5 |
5 |
5 |
5 |
5 |
5 |
B |
5 |
5 |
5 |
5 |
5 |
5 |
|
C |
5 |
5 |
5 |
5 |
5 |
5 |
|
D |
5 |
5 |
5 |
5 |
5 |
5 |
|
Total introduced |
20 |
20 |
20 |
20 |
20 |
20 |
|
24 |
A |
0 |
0 |
2 |
4 |
4 [2] |
5 |
B |
0 |
0 |
0 [2] |
4 [2] |
5 |
5 |
|
C |
0 |
0 |
0 |
4 [5] |
5 [2] |
5 |
|
D |
0 |
0 |
1 |
5 [1] |
5 |
5 [5] |
|
Total immobilised |
0 |
0 |
3 |
17 |
19 |
20 |
|
Effect % |
0 |
0 |
15 |
85 |
95 |
100 |
|
|
|
|
|
|
|
||
48 |
A |
0 |
0 |
2 [2] |
5 |
5 |
5 |
B |
0 |
0 |
2 |
5 |
5 |
5 |
|
C |
0 |
0 |
3 [3] |
5 |
5 |
5 |
|
D |
0 |
0 |
4 |
5 |
5 |
5 |
|
Total immobilised |
0 |
0 |
11 |
20 |
20 |
20 |
|
Effect % |
0 |
0 |
55 |
100 |
100 |
100 |
[ ]: number of daphnids observed trapped at the surface of the test solutions. These organisms were reimmersed into the respective solutions before recording of mobility.
( ): Mean concentration (mg/L)
(-): Not detected
Table 2: Mean concentrations
Cedryl Acetate, WAF prepared at x mg/L |
Mean measured concentration (mg/L) |
Mean concentration (mg/L) |
|
t = 0 – 24 h |
t = 24 – 48 h |
t = 0 – 48 h |
|
2.2 |
0.230 |
0.175 |
0.20 |
4.6 |
0.489 |
0.209 |
0.35 |
10 |
0.691 |
0.576 |
0.63 |
22 |
0.814 |
1.90 |
1.4 |
46 |
2.80 |
0.699 |
1.7 |
Table 3: Measured concentrations
Time of sampling |
Loading rate1 |
Concentration analysed |
Relative to initial |
[hours] |
[mg/L] |
[mg/L] |
[%] |
|
|
|
|
0 |
0 |
n.d. |
|
|
2.2 |
0.277 |
|
|
4.6 |
0.569 |
|
|
10 |
0.805 |
|
|
22 |
0.943 |
|
|
46 |
3.19 |
|
|
|
|
|
24 (old) |
0 |
n.d. |
n.a. |
|
2.2 |
0.191 |
69 |
|
4.6 |
0.420 |
74 |
|
10 |
0.593 |
74 |
|
22 |
0.703 |
75 |
|
46 |
2.46 |
77 |
|
|
|
|
24 (fresh) |
0 |
n.d. |
|
|
2.2 |
0.179 |
|
|
4.6 |
0.184 |
|
|
10 |
0.575 |
|
|
22 |
3.69 |
|
|
46 |
0.665 |
|
|
|
|
|
48 (old) |
0 |
n.d. |
n.a. |
|
2.2 |
0.172 |
96 |
|
4.6 |
0.237 |
129 |
|
10 |
0.577 |
100 |
|
22 |
0.975 |
26 |
|
46 |
0.735 |
111 |
|
|
|
|
1 A water accommodated fraction (WAF) separately prepared at the loading rate.
n.d. Not detected.
n.a. Not applicable.
Cumulative Immobilization Data and Observations in the Definitive Test
Geometric mean measured Concentration [mg/L] |
No. of Daphnia tested |
No. of immobilized Daphnia after |
% of immobilized Daphnia after |
||
24 h |
48 h |
24 h |
48 h |
||
|
|
||||
Control |
20 |
0 |
0 |
0 |
0 |
0.008 |
20 |
0 |
0 |
0 |
0 |
0.014 |
20 |
0 |
0 |
0 |
0 |
0.029 |
20 |
0 |
0 |
0 |
0 |
0.059 |
20 |
0 |
7 |
0 |
35 |
0.141 |
20 |
0 |
10 |
0 |
50 |
Summary of Analytical Results
Nominal Test Concentration |
Fresh test media Test Concentration |
Aged test media Test Concentration |
Geometric Mean Test Concentration |
|
[mg/L]1 |
[mg/L]2 |
[mg/L]3 |
Control |
n.a. |
n.a. |
n.a. |
WAF 1:16 |
0.014 |
0.005* |
0.008 |
WAF 1:8 |
0.022 |
0.008* |
0.014 |
WAF 1:4 |
0.043 |
0.020 |
0.029 |
WAF 1:2 |
0.088 |
0.039 |
0.059 |
WAF of 300 mg test item/L |
0.196 |
0.101 |
0.141 |
1initial mean measured: mean value of all freshly prepared test media per treatment group
2mean value of all aged test media per treatment group
3geometric mean value calculated using initial mean recovery and aged mean recovery rates per treatment group
*half the Limit of Quantification (LOQ) was used for the aged test item concentrations where the values were below the LOQ, as permitted by the OECD 23 guideline
n.a.: not applicable
Description of key information
The short-term toxicity to aquatic invertebrates for Cedryl Acetate EOA is based on read-across from the close structural analogues Cedryl Acetate 'mono' (CAS# 77-54-3) and Longifolene Coeur (CAS# 475-20-7). The information of Longifolene Coeur is uses as key being the lowest value.
Acute Daphnia
For Cedryl Acetate 'mono', a study was performed to assess the acute toxicity of the substance to Daphnia magna. The study was conducted in accordance with OECD Guideline for Testing of Chemicals No. 202 under semi-static conditions. Based on the results of a combined limit/range-finding test, the following nominal concentrations were tested in the definitive test: WAFs prepared separately at loading rates of 2.2, 4.6, 10, 22 and 46 mg/L. For each concentration and a control group, twenty Daphnia magna (less than 24 hours old) were exposed for 48 hours in air-tight closed vessels. Samples taken from all concentrations at the start and the end of both 24-hour renewal periods were analysed with a validated GC-FID method. Measured concentrations at the end of the renewal periods ranged from 69-111% relative to initial analysed concentrations, except for the 4.6 mg/L and 22 mg/L concentrations prepared for the second renewal period, where the concentrations were above and much below, relative to the initial analysed concentrations (129 and 26%, respectively). Based on these results, the mean measured concentrations were calculated. The range tested based on mean concentrations was 0.2, 0.35, 0.63, 1.4 and 1.7 mg/L. The 48h-EC50 value determined for Daphnia magna was 0.33 mg/L based on mean measured concentrations.
For Longifolene Coeur, a study was performed to assess the acute toxicity of the substance to Daphnia magna. The study was conducted in accordance with OECD Guideline for Testing of Chemicals No. 202 and GLP under semi-static conditions. Based on the results of a range-finding test, the following nominal concentrations were tested in the definitive test: untreated control, a water accommodated fraction (WAF) prepared at a nominal loading rate of 300 mg test item/L as highest test concentration and dilutions of the highest concentrations of 1:2, 1:4, 1:8 and 1:16. For each concentration and a control group, twenty Daphnia magna (less than 24 hours old) were exposed for 48 hours in air-tight closed vessels. The incidence of immobilisation was recorded for each test and control group at 24 hours and at 48 hours. Samples taken from all concentrations at the start and the end of both 24 -hour renewal periods were analysed with a validated GC-FID method. Measured concentrations in used test solutions ranged from 29 -49% of initial in the first renewal period, and from 26 -58% of initial in the second renewal period. Since test concentrations did not remain stable during the 24 -hour renewal periods (i.e. not within 80 -120% of initial), geometric mean measured concentrations were calculated. The range tested based on geometric mean measured concentrations was 0.141, 0.059, 0.029, 0.014 and 0.008 mg test item/L. The 48h-EC50 value to Daphnia magna was 0.119 mg/L based on geometric mean measured concentrations.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.119 mg/L
Additional information
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