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EC number: 701-122-3 | CAS number: 106185-75-5
- 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:
- 15 September 2016 to 14 December 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 211 (Daphnia magna Reproduction Test)
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 05 March 2015
- Specific details on test material used for the study:
- Physico-chemical Properties:
Specific Gravity: 0.916 at 20°C
Vapour Pressure: 0.0424 Pa (25 °C)
Solubility in water: 25.83 mg.L-1 (slow-stirring method)
log Kow: 4.4 at 35°C (HPLC Method) - Analytical monitoring:
- yes
- Details on sampling:
- Single samples for analysis were taken from the control and all test concentrations three times a week at renewal of the test media.
Samples for fresh solutions were taken from each treatment prior to addition of the daphnids and the suspension of algal cells.
Samples for old solutions were centrifuged at 500 g for 5 min (in order to pellet algal cells) before sampling of the supernatant.
Moreover, abiotic series of old solutions were analysed at day 5, 10 and 21 in order to assess the abiotic stability of the test substance during the test period compared to that in the biotic samples. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: slow stirring
- Controls: Test water without test substance but treated in the same way as the test substance solutions. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Strain/clone: Clone 5
- Source: LIEBE - CNRS UMR 7146 - UFR SciFA
- Age of parental stock (mean and range, SD): < 24 hours old
- Feeding: Daphnids will be fed with a suspension of algal cells (Pseudokirchneriella subcapitata) up to 0.1-0.2 mg C.Daphnia.-1day.-1 and at least three times a week during test. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 21 d
- Remarks on exposure duration:
- None
- Post exposure observation period:
- Not applicable
- Hardness:
- Hardness was approximately 250 mg CaCO3.L-1 (above 140 mg CaCO3.L-1 as recommended).
- Test temperature:
- Between 20.6 and 21.0 °C throughout the test (average value: 20.8 °C).
This is within the recommended range 20 +/- 2 °C. - pH:
- Between 7.80 and 8.84 throughout the test. This is withint the recommended range 6.0-9.0.
- Dissolved oxygen:
- Always > 7 mg/L
- Salinity:
- NA
- Nominal and measured concentrations:
- Nominal: 0.10, 0.18, 0.32, 0.56 and 1.00 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: All-glass sealed with screw cap test bottles (air-tight) of approximately 100 mL capacity. Each test vessel was uniquely identified with study code, replicate number, date of experimentation and concentration.
- Aeration: No aeration of the test solutions occurred throughout the test.
- Renewal rate of test solution: Semi-static, with three media changes per week; at each renewal, a new series of clean and sterilised test vessels were used.
- No. of animals: 10 animals individually held at each test concentration and the control series
- Loading: 1 daphnid per test vessel each completely filled with test solution and with headspace limited as much as possible
- Introduction of Daphnids: Daphnids were introduced into the test medium immediately after filling the test bottles with test solutions and algal cells
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted water as prescribed by the OECD Guideline 202
OTHER TEST CONDITIONS
- Photoperiod: 16 h light : 8 h dark
EFFECT PARAMETERS MEASURED:
- Offspring: The living offspring produced by each parent animal were removed and counted daily from the appearance of the first brood. Only the number of living offspring was counted, but the presence of aborted eggs or dead offspring was also recorded.
- Mortality: Mortality among the parent animals was recorded daily, at the same times as offspring were counted.
- Individual length of adults: At the end of the test the length of the adults was measured by microscopy using an ocular micrometer calibrated with a stage micrometer.
- Dissolved O2, hardness, pH: Measured at every media change in fresh and old media, in a single replicate for each treatment group.
- Temperature of Medium: Measured continuously in a vessel next to the test vessels, over the study period, beginning at the start of the test. Moreover, temperature was recorded at every media change in fresh and old media, in a single replicate for each treatment group (before pH, hardness and dissolved O2 determinations).
- Light intensity: Light intensity was measured once a week.
Test conditions were recorded with suitable instruments and documented in the raw data.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: ca. 1.78
- Nominal concentrations: 0.10; 0.18; 0.32; 0.56; 1.00
- Based on the results of an acute toxicity test on D. magna, test solutions used in the definitive test were prepared by direct addition of the required amounts of stock solution to test water to obtain the nominal concentrations - Reference substance (positive control):
- not specified
- Key result
- Duration:
- 21 d
- Dose descriptor:
- EC10
- Effect conc.:
- 0.589 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Remarks on result:
- other: 95% confidence limits: 0.323 - 1.073 mg test item/L
- Duration:
- 21 d
- Dose descriptor:
- other: EC20
- Effect conc.:
- 0.651 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Remarks on result:
- other:
- Remarks:
- 95% confidence limits: 0.363 - 1.186 mg test item/L
- Duration:
- 21 d
- Dose descriptor:
- EC50
- Effect conc.:
- 0.788 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Remarks on result:
- other:
- Remarks:
- 95% confidence limits: 0.381 - 1.631 mg test item/L
- Duration:
- 21 d
- Dose descriptor:
- LOEC
- Effect conc.:
- 0.84 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Key result
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.48 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Details on results:
- The effect of a chronic exposure to the test item on the reproduction of Daphnia magna was tested using five concentrations arranged in a geometric series, spaced by a factor of approximately 1.78.
Please, see the tables in the next section for the detailed results.
As said previously, toxicity was based on the time-weighted mean concentrations.
The evaluation of the concentration-effect-relationships and the calculations of effect concentrations were determined by the computer program ToxRat - Validity criteria fulfilled:
- yes
- Conclusions:
- The effects of a chronic exposure to test item 2-ETHYL-4-(2,2,3-TRIMETHYL-3-CYCLOPENTENE-1-YL)-(2E)-BUTEN-1-OL on the reproduction of Daphnia magna was investigated in this study. The evaluation was based on the time-weighted mean concentrations. Under the experimental conditions and after 21 days, the NOEC value estimated for the most sensitive endpoint cumulative number of offspring was 0.48 mg test item.L-1.
- Executive summary:
A study was performed to assess the effects of a chronic exposure to test item 2-ETHYL-4-(2,2,3-TRIMETHYL-3-CYCLOPENTENE-1-YL)-(2E)-BUTEN-1-OL on the reproduction of the freshwater crustacean Daphnia magna. The method followed was designed to be compliant with the OECD Guideline for Testing of Chemicals No. 211, "Daphnia magna, Reproduction Test", referenced as Method C.20 of Commission Regulation No. 440/2008 (amended byCommission Regulation (EU) 2016/266).
Based on the results of an acute toxicity test on D. magna (LPL Project D15-011; 48h-EC50= 1.34 mg.L-1), daphnids were exposed to an aqueous solution of the test item at the required nominal test concentrations of 0.10, 0.18, 0.32, 0.56 and 1.00 mg test item.L-1and to an untreated control for a total period of 21 days in closed vessels. Each treatment group consisted of 10 replicates each of one Daphnia magna (one individual per replicate). The test media was renewed three times a week and the daphnids were fed five days a week. Effects on reproductive performance were investigated by counting the living offspring produced by each parent animal every day. Mortality among the parent animals was also recorded. The concentrations of the test item were determined by chemical analyses three times a week at renewal of the test media.
Although every effort was made to maintain the concentrations of the test item (renewal of the test solutions, closed conditions with minimum headspace), the loss of the substance was sometimes greater than 20% of the measured initial concentration. The losses were probably caused by adsorption and degradation of the test item by food algae. Since the deviation of the exposure concentrations of the test substance was greater than 20% of the initial concentrations, the results were expressed in terms of time-weighted mean concentrations for the present study: 0.06, 0.14, 0.24, 0.48 and 0.84 mg test item.L-1. The effect of the test item on the reproduction of Daphnia magna after 21 days of exposure was as follows:
Critical effect and threshold concentration on cumulative offspring per surviving parent after 21 days
(mg test item.L-1)
95% confidence limits
(mg test item.L-1)
EC10
0.589
0.323 – 1.073
EC20
0.651
0.363 – 1.186
EC50
0.788
0.381 – 1.631
LOEC
0.840
-
NOEC
0.480
-
The effects of a chronic exposure to test item 2-ETHYL-4-(2,2,3-TRIMETHYL-3-CYCLOPENTENE-1-YL)-(2E)-BUTEN-1-OL on the reproduction of Daphnia magna was investigated in this study. The evaluation was based on the time-weighted mean concentrations. Under the experimental conditions and after 21 days, the NOEC value estimated for the most sensitive endpoint cumulative number of offspring was 0.48 mg test item.L-1.
Reference
Validity criteria:
Mortality: The mortality of the parent animals did not exceed 20 % at the end of the test in the controls.
Offspring: The mean number of live offspring produced per parent animal surviving in the controls at the end of the test was ≥ 60.
Thus all validity criteria for the performance of the controls have been fulfilled in the present study.
The following tables shows the No. Live Offspring per Replicate and Day:
Controls |
Day |
|||||||||||||||
Replicate |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
Total |
1 |
0 |
n.d. |
n.d. |
4 |
0 |
14 |
0 |
15 |
n.d. |
n.d. |
21 |
0 |
0 |
0 |
28 |
82 |
2 |
0 |
n.d. |
n.d. |
9 |
0 |
12 |
0 |
13 |
n.d. |
n.d. |
17 |
0 |
0 |
0 |
21 |
72 |
3 |
0 |
n.d. |
n.d. |
0 |
0 |
14 |
0 |
15 |
n.d. |
n.d. |
21 |
0 |
0 |
0 |
26 |
76 |
4 |
0 |
n.d. |
n.d. |
12 |
0 |
0 |
0 |
12 |
n.d. |
n.d. |
14 |
0 |
15 |
0 |
0 |
53 |
5 |
0 |
n.d. |
n.d. |
11 |
0 |
0 |
0 |
11 |
n.d. |
n.d. |
17 |
0 |
15 |
0 |
10 |
64 |
6 |
0 |
n.d. |
n.d. |
9 |
0 |
16 |
0 |
15 |
n.d. |
n.d. |
19 |
0 |
0 |
0 |
23 |
82 |
7 |
0 |
n.d. |
n.d. |
0 |
0 |
0 |
0 |
0 |
n.d. |
n.d. |
7 |
0 |
14 |
0 |
27 |
48 |
8 |
0 |
n.d. |
n.d. |
8 |
0 |
16 |
0 |
18 |
n.d. |
n.d. |
14 |
0 |
0 |
0 |
24 |
80 |
9 |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
- |
10 |
0 |
n.d. |
n.d. |
11 |
0 |
14 |
0 |
8 |
n.d. |
n.d. |
16 |
0 |
21 |
0 |
0 |
70 |
|
Mean Offspring Number:69.7 |
0.06 mg.L-1 |
Day |
|||||||||||||||
Replicate |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
Total |
1 |
0 |
n.d. |
n.d. |
11 |
0 |
1 |
0 |
7 |
n.d. |
n.d. |
10 |
0 |
20 |
0 |
0 |
49 |
2 |
0 |
n.d. |
n.d. |
6 |
0 |
11 |
0 |
16 |
n.d. |
n.d. |
17 |
0 |
1 |
0 |
10 |
61 |
3 |
0 |
n.d. |
n.d. |
3 |
0 |
16 |
0 |
8 |
n.d. |
n.d. |
13 |
0 |
0 |
0 |
24 |
64 |
4 |
0 |
n.d. |
n.d. |
3 |
0 |
19 |
0 |
13 |
n.d. |
n.d. |
8 |
0 |
15 |
0 |
21 |
79 |
5 |
0 |
n.d. |
n.d. |
11 |
0 |
0 |
0 |
14 |
n.d. |
n.d. |
16 |
0 |
14 |
0 |
0 |
55 |
6 |
0 |
n.d. |
n.d. |
12 |
0 |
0 |
0 |
16 |
n.d. |
n.d. |
19 |
0 |
13 |
0 |
0 |
60 |
7 |
0 |
n.d. |
n.d. |
12 |
0 |
3 |
0 |
12 |
n.d. |
n.d. |
13 |
0 |
16 |
0 |
27 |
83 |
8 |
0 |
n.d. |
n.d. |
8 |
0 |
16 |
0 |
19 |
n.d. |
n.d. |
22 |
0 |
0 |
0 |
0 |
65 |
9 |
0 |
n.d. |
n.d. |
9 |
0 |
0 |
0 |
12 |
n.d. |
n.d. |
17 |
0 |
18 |
0 |
0 |
56 |
10 |
0 |
n.d. |
n.d. |
6 |
0 |
15 |
0 |
0 |
n.d. |
n.d. |
12 |
0 |
12 |
0 |
21 |
66 |
|
Mean Offspring Number:63.8 |
0.14 mg.L-1 |
Day |
|||||||||||||||
Replicate |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
Total |
1 |
0 |
n.d. |
n.d. |
8 |
0 |
17 |
0 |
0 |
n.d. |
n.d. |
10 |
0 |
5 |
0 |
0 |
40 |
2 |
0 |
n.d. |
n.d. |
9 |
0 |
12 |
0 |
5 |
n.d. |
n.d. |
13 |
0 |
14 |
0 |
17 |
70 |
3 |
0 |
n.d. |
n.d. |
0 |
0 |
0 |
0 |
0 |
n.d. |
n.d. |
17 |
0 |
0 |
0 |
16 |
33 |
4 |
0 |
n.d. |
n.d. |
8 |
0 |
14 |
0 |
6 |
n.d. |
n.d. |
14 |
0 |
18 |
0 |
21 |
81 |
5 |
0 |
n.d. |
n.d. |
0 |
0 |
0 |
0 |
9 |
n.d. |
n.d. |
16 |
0 |
0 |
0 |
18 |
43 |
6 |
0 |
n.d. |
n.d. |
0 |
0 |
9 |
0 |
8 |
n.d. |
n.d. |
16 |
0 |
0 |
0 |
24 |
57 |
7 |
0 |
n.d. |
n.d. |
8 |
0 |
16 |
0 |
1 |
n.d. |
n.d. |
11 |
0 |
13 |
0 |
16 |
65 |
8 |
0 |
n.d. |
n.d. |
5 |
0 |
15 |
0 |
14 |
n.d. |
n.d. |
18 |
0 |
0 |
0 |
18 |
70 |
9 |
0 |
n.d. |
n.d. |
9 |
0 |
13 |
0 |
0 |
n.d. |
n.d. |
10 |
0 |
20 |
0 |
20 |
72 |
10 |
0 |
n.d. |
n.d. |
1 |
0 |
4 |
0 |
10 |
n.d. |
n.d. |
17 |
0 |
0 |
0 |
23 |
55 |
|
Mean Offspring Number:58.6 |
0.24 mg.L-1 |
Day |
|||||||||||||||
Replicate |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
Total |
1 |
0 |
n.d. |
n.d. |
8 |
0 |
11 |
0 |
18 |
n.d. |
n.d. |
20 |
0 |
0 |
0 |
14 |
71 |
2 |
0 |
n.d. |
n.d. |
6 |
0 |
18 |
0 |
17 |
n.d. |
n.d. |
18 |
0 |
1 |
0 |
0 |
60 |
3 |
0 |
n.d. |
n.d. |
8 |
0 |
12 |
0 |
0 |
n.d. |
n.d. |
12 |
0 |
11 |
0 |
3 |
46 |
4 |
0 |
n.d. |
n.d. |
16 |
0 |
1 |
0 |
15 |
n.d. |
n.d. |
15 |
0 |
14 |
0 |
0 |
61 |
5 |
0 |
n.d. |
n.d. |
8 |
0 |
16 |
0 |
16 |
n.d. |
n.d. |
7 |
0 |
18 |
0 |
25 |
90 |
6 |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
- |
7 |
0 |
n.d. |
n.d. |
9 |
0 |
17 |
0 |
0 |
n.d. |
n.d. |
4 |
0 |
15 |
0 |
20 |
65 |
8 |
0 |
n.d. |
n.d. |
10 |
0 |
17 |
0 |
0 |
n.d. |
n.d. |
8 |
0 |
12 |
0 |
12 |
59 |
9 |
0 |
n.d. |
n.d. |
13 |
0 |
1 |
0 |
12 |
n.d. |
n.d. |
10 |
0 |
10 |
0 |
0 |
46 |
10 |
0 |
n.d. |
n.d. |
8 |
0 |
17 |
0 |
0 |
n.d. |
n.d. |
12 |
0 |
16 |
0 |
12 |
65 |
|
Mean Offspring Number:62.6 |
0.48 mg.L-1 |
Day |
|||||||||||||||
Replicate |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
Total |
1 |
0 |
n.d. |
n.d. |
13 |
0 |
0 |
0 |
15 |
n.d. |
n.d. |
14 |
0 |
17 |
0 |
0 |
59 |
2 |
0 |
n.d. |
n.d. |
6 |
0 |
15 |
0 |
16 |
n.d. |
n.d. |
15 |
0 |
0 |
0 |
22 |
74 |
3 |
0 |
n.d. |
n.d. |
0 |
0 |
6 |
0 |
10 |
n.d. |
n.d. |
14 |
0 |
0 |
0 |
17 |
47 |
4 |
0 |
n.d. |
n.d. |
5 |
0 |
13 |
0 |
18 |
n.d. |
n.d. |
20 |
0 |
2 |
0 |
27 |
85 |
5 |
0 |
n.d. |
n.d. |
2 |
0 |
16 |
0 |
17 |
n.d. |
n.d. |
20 |
0 |
0 |
0 |
17 |
72 |
6 |
0 |
n.d. |
n.d. |
3 |
0 |
13 |
0 |
5 |
n.d. |
n.d. |
8 |
0 |
18 |
0 |
21 |
68 |
7 |
0 |
n.d. |
n.d. |
7 |
0 |
9 |
0 |
17 |
n.d. |
n.d. |
19 |
0 |
2 |
0 |
18 |
72 |
8 |
0 |
n.d. |
n.d. |
1 |
0 |
8 |
0 |
12 |
n.d. |
n.d. |
13 |
0 |
15 |
0 |
7 |
56 |
9 |
0 |
n.d. |
n.d. |
0 |
0 |
0 |
0 |
0 |
n.d. |
n.d. |
7 |
0 |
16 |
0 |
0 |
23 |
10 |
0 |
n.d. |
n.d. |
4 |
0 |
14 |
0 |
17 |
n.d. |
n.d. |
15 |
0 |
0 |
0 |
20 |
70 |
|
Mean Offspring Number:62.6 |
0.84 mg.L-1 |
Day |
|||||||||||||||
Replicate |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
Total |
1 |
0 |
n.d. |
n.d. |
0 |
0 |
7 |
0 |
3 |
n.d. |
n.d. |
10 |
0 |
0 |
0 |
3 |
23 |
2 |
0 |
n.d. |
n.d. |
1 |
0 |
8 |
0 |
0 |
n.d. |
n.d. |
3 |
0 |
2 |
0 |
13 |
27 |
3 |
0 |
n.d. |
n.d. |
7 |
0 |
0 |
0 |
11 |
n.d. |
n.d. |
0 |
0 |
0 |
0 |
0 |
18 |
4 |
0 |
n.d. |
n.d. |
0 |
0 |
3 |
0 |
10 |
n.d. |
n.d. |
11 |
0 |
2 |
0 |
4 |
30 |
5 |
0 |
n.d. |
n.d. |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
- |
6 |
0 |
n.d. |
n.d. |
0 |
0 |
0 |
0 |
M |
M |
M |
M |
M |
M |
M |
M |
- |
7 |
0 |
n.d. |
n.d. |
0 |
0 |
5 |
0 |
6 |
n.d. |
n.d. |
4 |
0 |
M |
M |
M |
- |
8 |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
- |
9 |
0 |
n.d. |
n.d. |
0 |
0 |
4 |
0 |
8 |
n.d. |
n.d. |
5 |
0 |
5 |
0 |
4 |
26 |
10 |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
M |
- |
|
Mean Offspring Number:24.8 |
“M”: dead females
n.d.: not determined (weekend)
The next table shows the Parental Daphnia magna lengths at the end of the test after 21 days (mm)
Replicate |
Time-Weighted Mean Concentration(mg test item.L-1) |
|||||
Control |
0.06 |
0.14 |
0.24 |
0.48 |
0.84 |
|
1 |
3.75 |
3.50 |
3.50 |
3.50 |
3.75 |
3.50 |
2 |
3.75 |
3.50 |
3.50 |
3.50 |
3.50 |
3.25 |
3 |
3.75 |
3.50 |
3.00 |
3.50 |
3.75 |
3.25 |
4 |
3.75 |
3.50 |
3.75 |
3.50 |
3.75 |
3.50 |
5 |
3.75 |
3.25 |
3.25 |
4.00 |
3.75 |
M |
6 |
3.75 |
3.50 |
3.75 |
M |
3.50 |
M |
7 |
3.75 |
3.50 |
3.75 |
3.75 |
3.50 |
M |
8 |
4.00 |
3.75 |
3.75 |
3.50 |
3.50 |
M |
9 |
M |
3.50 |
3.50 |
3.50 |
3.00 |
3.5 |
10 |
3.75 |
3.50 |
3.50 |
3.75 |
3.75 |
M |
Description of key information
A reliable study performed with GLP according to the OECD 211 guideline was available.
According to this study, the 21d-NOEC was 0.48 mg/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.48 mg/L
Additional information
One QSAR data that determined the long-term toxicity to aquatic invertebrates was available and confirmed the GLP experimental study.
This QSAR prediction was performed to assess the chronic toxicity of test item 2-ethyl-4-(2,2,3-trimethyl-3-cyclopenten-1-yl)-(2E)-buten-1-ol to daphnid. This QSAR has been validated to be compliant with the OECD recommendations for QSAR modeling (OECD, 2004) and predicts the endpoint value which would be expected when testing the substance under experimental conditions in a laboratory following Guideline for Testing of Chemicals No. 211, "Daphnia magna Reproduction Test" (1). The criterion predicted was the NOEC (No Observed Effect Concentration), a tested concentration which is expected to cause no effect on reproducibility within a period of 21 days. The substance falls within the applicability domain of the model as demonstrated in the QPRF.
The 21d-NOEC = 0.14 mg test item/L with 95%-Confidence Limit of 0.10 -0.18 mg test item/L. The NOEC was based on effects on reproduction.
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