Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Ecotoxicological information

Short-term toxicity to aquatic invertebrates

Currently viewing:

Administrative data

Link to relevant study record(s)

Reference
Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
key study
Study period:
17 January 2018 to 19 January 2018
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
Deviations:
yes
Remarks:
no analytics were performed because it was not possible to develop a suitable analytical method
GLP compliance:
yes (incl. QA statement)
Analytical monitoring:
no
Remarks:
it was imposible to develop a suitable analytical method
Vehicle:
yes
Details on test solutions:
A primary stock concentrate of the substance, with a nominal concentration of 10 g/L, was prepared by weighing a nominal 0.1 g of test substance (actual weight: 0.10000 g) into a 10 mL volumetric flask and making up to volume with tetrahydrofuran (THF). The stock was then manually shaken to mix. The resultant stock was observed to be clear and colourless and was used to prepare the test solutions.
Total amount of THF present in the test solutions 100 ug/L.
Test organisms (species):
Daphnia magna
Details on test organisms:
TEST ORGANISM
- Common name: Daphmia magna
- Source: laboratory cultures held at Scymaris.
- Age of parental stock (mean and range, SD): 22 ± 1 days (daphnids in test < 24 h)
- Feeding during test: none

ACCLIMATION
- Stock conditions (same as test or not): yes
- Type and amount of food: mixed algae diet of Chlorella vulgaris, strain CCAP 211/12 and Pseudokirchneriella subcapitata, strain CCAP 278/4
- Feeding frequency: daily ad libitum
- Health during acclimation: no evidence of diease before test:

Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
48 h
Hardness:
248.7 as CaCO2
Test temperature:
19.1-20.2 ˚C
pH:
7.76-8.01
Dissolved oxygen:
9.05-9.35 mg/L
Nominal and measured concentrations:
nominal: 0.0625, 0.125, 0.25, 0.5 and 1.0 mg/L (maximum based on solubility)
Details on test conditions:
TEST SYSTEM
- Test vessel: Glass beakers of 250 mL
- Type (delete if not applicable):closed
- Fill volume: 200 mL
- Aeration: 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): 4

TEST MEDIUM / WATER PARAMETERS: The reconstituted water medium used for testing (and maintenance of stock cultures) was Elendt's M4 D. magna medium

OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16/8

EFFECT PARAMETERS MEASURED : immobilisation at 24 and 48 h

VEHICLE CONTROL PERFORMED: yes

RANGE-FINDING STUDY: highest concentration limited by solubility in water
concentrations tested : 0.0625, 0.125, 0.25, 0.5 and 1.0 mg/L (max THF 100 ug/L)
results: immobility: 0, 0, 0, 20 and 20% at 0.0625, 0.125, 0.25, 0.5 and 1.0 mg/L
behaviour: Daphnia in 0.25, 0.5 and 1.0 mg/L test concentrations showed reduced movement compared to controls. At 0.5 and 1.0 mg/L 4/10 daphnids were at the surface
Reference substance (positive control):
no
Duration:
48 h
Dose descriptor:
EC50
Effect conc.:
> 1 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Details on results:
Daphnids in the 0.5 and 1.0 mg/L test concentrations were observed as less active compared to the controls.
At the 48 hour time point, the two immobile daphnids in 0.5 mg/L replicates A and D were observed to be still alive as they were twitching. The immobile daphnid in 0.5 mg/L replicate C was on the surface of the solution.

Daphnia magna response

Time

(hour)

Nominal 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

20

0

0

Solvent Control

0

0

0

0

20

0

0

0.0625

0

0

0

0

20

0

0

0.125

0

0

0

0

20

0

0

0.25

0

0

0

0

20

0

0

0.5

0

0

0

0

20

0

0

1.0

0

0

0

0

20

0

0

48

Control

0

0

0

0

20

0

0

Solvent Control

0

0

0

0

20

0

0

0.0625

0

0

0

0

20

0

0

0.125

0

0

0

0

20

0

0

0.25

0

1

0

0

20

1

5

0.5

1

1

1

1

20

4

20 *

1.0

1

2

0

0

20

3

15

 * Significant difference (p <0.05) from the control. LOEC value not affected, see section 5.1.


Validity criteria fulfilled:
yes
Conclusions:
The EC50 for Daphnia magna is > 1.0 mg/L
Executive summary:

Due to the low solubility of the substance, a 1 mg/L test concentration was selected as the highest concentration based on a non-GLP range finding study. The test substance was dosed to the media via a solvent carrier (tetrahydrofuran (THF)) to assist in dosing the test compound. The concentration of solvent used in all exposure solutions with the exception of the control was 100 µL/L.

Daphnids were exposed during 48 h (static test) to control, Solvent Control and nominal concentrations of 0.0625, 0.125, 0.25, 0.5 and 1.0 mg/L. No confirmatory analysis of the test solutions was performed due to lack of an analytical method.

The EC50 is >1.0 mg/L. Based on immobility compared to the control (p <0.05) the 48h NOEC was determined to be 1.0 mg/L. Immobility in the 0.5 mg/L test concentration was significantly different (p <0.05) from the control. However, as immobility in the 1.0 mg/L test concentration was not significantly different (p <0.05) from the control, the NOEC was not affected.

Description of key information

Daphnids were exposed during 48 h (static test) to control, solvent control and nominal concentrations of 0.0625, 0.125, 0.25, 0.5 and 1.0 mg/L. No confirmatory analysis of the test solutions was performed due to lack of an analytical method.

The EC50 is >1.0 mg/L. Based on immobility compared to the control (p <0.05) the 48h NOEC was determined to be 1.0 mg/L. Immobility in the 0.5 mg/L test concentration was significantly different (p <0.05) from the control. However, as immobility in the 1.0 mg/L test concentration was not significantly different (p <0.05) from the control, the NOEC was not affected.

Key value for chemical safety assessment

Fresh water invertebrates

Fresh water invertebrates
Effect concentration:
1 mg/L

Additional information