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Diss Factsheets

Ecotoxicological information

Short-term toxicity to aquatic invertebrates

Administrative data

Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2009-10-27 to 2010-04-07
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: GLP study, study is performed according to OECD and EU guidelines, no deviation from study plan.

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2010
Report date:
2010

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
EU Method C.2 (Acute Toxicity for Daphnia)
Deviations:
no
Qualifier:
according to guideline
Guideline:
OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
Deviations:
no
GLP compliance:
yes (incl. QA statement)

Test material

Constituent 1
Chemical structure
Reference substance name:
N-(2,2-dimethoxyethyl)prop-2-enamide
EC Number:
610-472-5
Cas Number:
49707-23-5
Molecular formula:
C7 H13 N1 O3
IUPAC Name:
N-(2,2-dimethoxyethyl)prop-2-enamide

Sampling and analysis

Analytical monitoring:
yes
Details on sampling:
- Concentrations: 1 ( 100 mg/L)
- Sampling method: no data
- Sample storage conditions before analysis: yes., storage < -10° C

Test solutions

Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: according to OECD 202 a limit test was conducted (dissolving 41.5mg of the test item into 415mL test water by intense stirring for 20 minutes).
- Controls: In the control, test water was used without addition of the test item
- Evidence of undissolved material (e.g. precipitate, surface film, etc): no evidende, acc. to water solubitlity the test item is fully miscible with water

Test organisms

Test organisms (species):
Daphnia magna
Details on test organisms:
TEST ORGANISM
- Common name: Water flea
- Strain: Clone 5
- Source: The Daphnia were bred in the laboratories of the testing facility under similar temperature and light conditions as used in the test. The test organisms were not first brood progeny.
- Age at study initiation (mean and range, SD): From 5.5 to 21.75 hours old
- Method of breeding: continous laboratory culture
- Feeding during test: no
- Food type: not applicable
- Amount: not applicable
- Frequency: not applicable

ACCLIMATION
- Acclimation period: not necessary, laboratory breed stock
- Acclimation conditions (same as test or not): see above
- Type and amount of food: Desmodesmus
- Feeding frequency: all working days
- Health during acclimation (any mortality observed): not applicable

Study design

Test type:
static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
48 h
Post exposure observation period:
no

Test conditions

Hardness:
Reconstituted Water, (Elendt M4):
Water Hardness: 2.5 mmol/L (= 250 mg/L) as CaCO3
Alkalinity: 0.9 mmol/L
Test temperature:
20 to 21 °C at test start;
20 °C at test end
pH:
7.9 at test start;
7.8 at test end; and thus the pH-value did not vary by more than 1.5 units
Dissolved oxygen:
8.7 - 8.8 mg/L at test start;
8.6 mg/L at test end
Nominal and measured concentrations:
see block "additional information on results"
Details on test conditions:
TEST SYSTEM
- Test vessel: beaker, 100 ml

- Material, size, headspace, fill volume: 80 ml
- Aeration: no
- Type of flow-through (e.g. peristaltic or proportional diluter): not applicable
- Renewal rate of test solution (frequency/flow rate): no
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- No. of vessels per vehicle control (replicates): not applicable

TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water
- Culture medium different from test medium: no
- Intervals of water quality measurement: no data

OTHER TEST CONDITIONS
- Adjustment of pH: no data
- Photoperiod: 16/8 l/d
- Light intensity: 330 - 550 lux

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : immobility

TEST CONCENTRATIONS
- Spacing factor for test concentrations: not applicable
- Range finding study: yes
- Test concentrations: 1-10-100 mg/L
- Results used to determine the conditions for the definitive study: yes
Reference substance (positive control):
no
Remarks:
historical data

Results and discussion

Effect concentrationsopen allclose all
Duration:
48 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
48 h
Dose descriptor:
LOEC
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
48 h
Dose descriptor:
NOEC
Effect conc.:
>= 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Details on results:
- Behavioural abnormalities: no
- Observations on body length and weight: no data
- Other biological observations: no
- Mortality of control: no
- Other adverse effects control: no
- Abnormal responses: 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: yes, in the range fining test. Therefore a solvent and lower concentrations were used in the definite test
Results with reference substance (positive control):
- Results with reference substance valid, as determined by historical and regularily conducted study
- Mortality: control: 0
- EC50/LC50: 1.59 (24 h) and 1.374 mg/L (48 h)
Reported statistics and error estimates:
not applicable due to no observed immobility

Any other information on results incl. tables

Nominal Concentration

No. of Daphnia tested

No. of immobilized Daphnia after

% of immobilized Daphnia after

[mg test item/L]

 

24 h

48 h

24 h

48 h

Control

20

0

0

0

0

100

20

0

0

0

0

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
The toxic effect of the test item N-(2,2-Dimethoxyethyl)acrylamide (NAAADA) to Daphnia magna was assessed in a static limit-test. The 48-hour NOEC was determined to be => 100 mg test item/L. The 48-hour EC50 value was calculated to be > 100 mg test item/L.
Executive summary:

After 48 hours of exposure no immobilisation of the test animals was observed in the control and the only test item concentration of nominal 100 mg/L.All validity criteria were met.

 

In the most recent test with the reference item potassium dichromate performed in January 2010 (study code 48399220) the EC50after 24 hours was determined to be 1.59 mg test item/L indicating that the sensitivity of the Daphnia was consistent with the level proposed by the OECD 202 guideline (EC50-24 h between 0.6 and 2.1 mg potassium dichromate/L).

The toxic effect of the test item N-(2,2-Dimethoxyethyl)acrylamide (NAAADA) to Daphnia magna was assessed in a static limit-test. The 48-hour NOEC was determined to be => 100 mg test item/L. The 48-hour EC50 value was calculated to be > 100 mg test item/L.