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Ecotoxicological information

Short-term toxicity to aquatic invertebrates

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Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2002-05-21 - 2002-06-13
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study with acceptable restrictions
Qualifier:
according to guideline
Guideline:
OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
Version / remarks:
1984
Qualifier:
according to guideline
Guideline:
EU Method C.2 (Acute Toxicity for Daphnia)
Version / remarks:
1992
GLP compliance:
yes (incl. QA statement)
Analytical monitoring:
yes
Details on sampling:
- Concentrations: All test concentrations at 0 h. For stability control a series of the concentrations tested, was made up in the same way as the concentrations for biological part, but in separate vessels without test organisms and NaHCO3.
Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A stock solution was prepared by adding 102 mg of the test item to 1 L synthetic freshwater without NaHCO3. For the biological part of the test, the stock solution was supplied with NaHCO3, to achieve the composition of synthetic water.
- Eluate: no
- Differential loading: no
- Controls: yes, test medium control

Test organisms (species):
Daphnia magna
Details on test organisms:
TEST ORGANISM
- Common name: waterflea
- Strain/clone: clone 5
- Age at study initiation (mean and range, SD): >24 h
- Source: originally obtained from Bayer AG, Leverkusen, Germany and bred in house
- Method of breeding: bred in M4 medium, fed daily with Desmodesmus subspicatus ad libitum.
- Feeding during test : no

ACCLIMATION
- Acclimation period: same as test
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
48 h
Hardness:
250 mg/L (CaCO3)
Test temperature:
20 °C ± 1 °C
pH:
7.6 - 8.2
Dissolved oxygen:
7.4 - 8.5 mg/L
Nominal and measured concentrations:
Nominal test concentrations: 0.15, 0.3, 0.6, 1.2, 2.5, 5, 10 mg/L

Stability control:
DOC analysis 0 h: < LOQ, < LOQ, < LOQ, < LOQ, 2.86, 5.76, 11.25 mg/L
DOC analysis 48 h:< LOQ, < LOQ, < LOQ, < LOQ, < LOQ, 4.77, 10.31 mg/L

Test concentrations:
DOC analysis 0 h: < LOQ, < LOQ, < LOQ, < LOQ, 2.8, 6.2, 12.4 mg/L
Details on test conditions:
TEST SYSTEM
- Test vessel: 22 mL head-space test tubes
- Fill volume: 20 mL
- Aeration: none
- 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: synthetic freshwater
- Ca/mg ratio: 4:1

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
Mobility after 0, 24 and 48 h
Reference substance (positive control):
yes
Remarks:
potassium dichromate
Duration:
48 h
Dose descriptor:
EC50
Effect conc.:
4.5 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
test mat.
Basis for effect:
mobility
Remarks on result:
other: confidence limits: 2.4 - 8.3 mg/L
Duration:
48 h
Dose descriptor:
EC100
Effect conc.:
> 12.4 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
48 h
Dose descriptor:
EC10
Effect conc.:
1.72 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
test mat.
Basis for effect:
mobility
Results with reference substance (positive control):
Reference item is tested quarterly:
1 mg K2 Cr2 O7 / L <= 50 % effect (<= EC50)
2 mg K2 Cr2 O7 / L >= 50 % effect ( >= EC50)
Reported statistics and error estimates:
The EC50 (48 h) was calculated by probit analysis according to Cavalli-Sforza (1972).

 Table 1: Biological effects

Concentration (mg/L)

number

Number mobile

Number immobile

%

Control

20

20

0

0

0.15

20

20

0

0

0.3

20

20

0

0

0.6

20

20

0

0

1.2

20

20

0

0

2.8

20

20

0

0

6.2

20

15

5

25

12.4

20

12

8

40

 

 

Validity criteria fulfilled:
yes
Conclusions:
An EC50 (48 h) of 4.5 mg/L based on measured concentrations (TOC analysis) was determined.
Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
other information
Study period:
1985
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
documentation insufficient for assessment
Qualifier:
according to guideline
Guideline:
other: AFNOR T 90 301
Version / remarks:
1983
GLP compliance:
not specified
Analytical monitoring:
not specified
Vehicle:
not specified
Test organisms (species):
Daphnia magna
Details on test organisms:
TEST ORGANISM
- Common name: water flea
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
24 h
Nominal and measured concentrations:
not indicated
Details on test conditions:
ratio Ca/Mg 4:1
conductivity equal to 250 mg/L ± 25 mg/L
Reference substance (positive control):
not specified
Duration:
24 h
Dose descriptor:
EC50
Effect conc.:
25 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Validity criteria fulfilled:
not specified
Conclusions:
The determined EC50 (24 h) was 25 mg/L.
Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
supporting study
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
documentation insufficient for assessment
Qualifier:
according to guideline
Guideline:
OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
Version / remarks:
1984
GLP compliance:
not specified
Analytical monitoring:
yes
Details on sampling:
- Sampling method: At the beginning of exposure, before water change
Test organisms (species):
Daphnia magna
Test type:
semi-static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
48 h
Test temperature:
20 ± 1 °C
Nominal and measured concentrations:
Nominal test substance concentrations: 2.96, 4.44, 6.67, 10.0, 15.0 mg/L
Details on test conditions:
TEST SYSTEM
- Fill volume: 200 mL
- Renewal rate of test solution (frequency): every 24 h
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4

OTHER TEST CONDITIONS
- Photoperiod: 16 hours light / 8 hours dark
- Light intensity: indoor light

EFFECT PARAMETERS MEASURED (with observation intervals if applicable): mobility after 24 and 48 h

Reference substance (positive control):
not specified
Duration:
48 h
Dose descriptor:
EC50
Effect conc.:
7.15 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Remarks on result:
other: 95% confidence limit: 6.30-8.06 mg/L
Duration:
48 h
Dose descriptor:
NOEC
Effect conc.:
4.44 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility

Description of key information

EC50 (48 h): 4.5 mg/L (meas. TOC, OECD 202)

Key value for chemical safety assessment

Additional information

The acute toxicity of the substance to Daphnia magna was investigated under static conditions in a guideline study according to OECD 202 (GLP). The test animals exposed to nominal test substance concentrations of 0.15, 0.3, 0.6, 1.2, 2.5, 5, 10, 100 mg/L for 48 h. An EC50 (48 h) of 4.5 mg/L (meas. initial based on TOC) was determined. A comparable result was obtained in a supporting study conducted according to OECD 202. Daphnia magna were exposed for 48 h to nominal test substance concentrations of 2.96, 4.44, 6.67, 10.0 and 15.0 mg/L. The test solutions were re-newed every 24 h and an analytical dose verfication by HPLC was performed. The determined EC50 (48 h) was 7.15 mg/L.

Supporting information is available from a study conducted according to AFNOR standard T 90 301N. In the study an EC50 (24 h) of 25 mg/L (nominal) was determined. However, since the test duration was only 24 h and the documentation of the study is not sufficient this result is not used for the assessment.