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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
key study
Study period:
28 February - 21 April 2017
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2017
Report date:
2017

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
Version / remarks:
13 April 2004
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.2 (Acute Toxicity for Daphnia)
Version / remarks:
30 May 2008
Deviations:
no
GLP compliance:
yes (incl. QA statement)

Test material

Constituent 1
Chemical structure
Reference substance name:
Disodium 2-oxoglutarate
EC Number:
206-167-8
EC Name:
Disodium 2-oxoglutarate
Cas Number:
305-72-6
Molecular formula:
C5H6O5.2Na
IUPAC Name:
disodium 2-oxopentanedioate
impurity 1
Chemical structure
Reference substance name:
Water
EC Number:
231-791-2
EC Name:
Water
Cas Number:
7732-18-5
Molecular formula:
H2O
IUPAC Name:
Oxidane
Test material form:
solid: crystalline
Remarks:
Crystalline powder
Details on test material:
Batch No: 14152300
Storage: 15 – 25 °C

Sampling and analysis

Analytical monitoring:
yes

Test solutions

Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION
The following test vessels were set up:
- Test solution (Tn); containing Daphnia medium with test item (two replicates with 20 Daphnia each)
- Blank control (Bn); containing pure Daphnia medium (three replicates with 20 Daphnia each)
Since the test item is soluble, the test solutions were prepared by directly dissolving the test item in Daphnia medium. The resulting solution was used as the test solution in the toxicity test. Pure Daphnia medium served as blank controls.
- O2 concentration and pH were measured in the test medium for each concentration including the blank control. If the O2 concentration was too low (>5.0 mg/l required) the media was aerated by stirring. Afterwards, the media were filled into the test vessels (50 ml per vessel).
- Daphnia, aged less than 24 h and already acclimatized to the Daphnia medium, were then introduced into the test media, and the vessels were covered with a glass plate. The Daphnia were not fed during the test and the test vessels were not aerated.
- Semi static conditions: After 24 h, the Daphnia were transferred to the fresh test media.
- Evidence of undissolved material: Not relevant. Since the test item is soluble, the test solutions were prepared by directly dissolving the test item in Daphnia medium. The resulting solution was used as the test solution in the toxicity test.

Test organisms

Test organisms (species):
Daphnia magna
Details on test organisms:
TEST ORGANISMS
- Test organism: Daphnia magna (Straus, 1820), derived from a healthy stock and not first brood progeny
- Breeding: Parental and young Daphnia held in 4 l glass aquaria (3 l medium) at 20±2 °C
- Illumination: 16 h per day
- Medium: Continuously aerated Elendt M4 medium prepared with ultra-pure water (conductivity <1.5 µS/cm)
- Feed: Suspension of Desmodesmus subspicatus in Elendt M4 medium with an optical density OD680 of about 15 units

Study design

Test type:
semi-static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
48 h

Test conditions

Hardness:
not reported
Test temperature:
18–22 °C, controlled at ±1 °C
pH:
6.9-8.3
Dissolved oxygen:
The minimum dissolved oxygen concentration in the controls and the test vessels at the end each 24h-period was >=7.3 mg O2/l (required >=3 mg O2/l).
Salinity:
not reported
Conductivity:
671 to 844 µS cm-1
Nominal and measured concentrations:
The concentrations of a-Ketoglutarate disodium salt in in the test medium were measured by HPLC analysis at the beginning and after 24 (in the old and fresh medium) and 48 h of exposure. These analyses revealed that the concentrations of test item were stable over each 24 h period and remained within the 80-120% of the nominal concentration. The measured concentration at the beginning of the test was 103 mg/l, and after 24 h in the old medium it was 100 mg/l (i.e. 98% of
initial). After renewal of the test media at 24h the measured concentration was 98.0 mg/l ; at the end of the test after 48 h it was 94.1 mg/l (i.e. 96% of fresh medium). Therefore, the effective concentrations ECx were assessed based on the nominal concentration of the test item.
Details on test conditions:
TEST SYSTEM
- Test vessel: 100 ml beakers, all-glass, with 50 ml of test medium,covered with a glass plate to avoid evaporation and contamination of the test solutions with dust
- Test medium: Elendt M4 medium; prepared with ultra-pure water (conductivity <1.5 µS/cm)
- Number of Daphnia: 40 individuals per test concentration, 20 per vessel
- Age: Less than 24 h
- Light: 16 h photoperiod a day, supplied by overhead white fluorescent tubes
- Temperature: 18–22 °C, controlled at ±1 °C
- pH: 6 to 9. The pH should normally not vary by more than 1.5 units in one test.
- Feed: The Daphnia are not fed during the test
- Aeration: The test vessels were not aerated during the test.
- Test type: Semi-static exposure conditions; renewal of test medium after 24 h of exposure
- Test duration: 48 h

RANGE-FINDING STUDY
Prior to the definitive test a non-GLP range finding test with nominal concentrations of 1, 10 and 100 mg/l of a-Ketoglutarate disodium salt was performed.

EFFECT PARAMETERS MEASURED
Observed immobility (inability to swim) of the daphnids: Since no significant effects were observed in the non-GLP range-finding test, the definitive test was
performed as a limit-test at 100 mg/l
Reference substance (positive control):
yes
Remarks:
Acute reference test with potassium dichromate conducted twice a year

Results and discussion

Effect concentrationsopen allclose all
Key result
Duration:
48 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Key result
Duration:
48 h
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
24 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
24 h
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Details on results:
No significant effects (<=10% immobilization) were observed at 100 mg/l nominal concentration or in the blank controls, neither after 24 h of exposure nor after 48 h. Therefore, the median effect concentrations (EC50) of a-Ketoglutarate disodium salt (CAS no. 305-72-6) on Daphnia magna after 24 h as well as after 48 h of exposure were estimated to be >100 mg/l nominal concentration.
The NOEC values after 24 h and after 48 h of exposure were both 100 mg/l nominal concentration.
Results with reference substance (positive control):
Acute ref. test with K2Cr2O7 conducted twice a year. The EC50 value for the control of sensitivity for 24 h of exposure with K2Cr2O7 was estimated to be 0.89 mg/l (29.6.2016), which lies within the recomm. range of 0.6–2.1 mg/l acc. to OECD Guideline 202.
Reported statistics and error estimates:
The effective concentrations ECx were assessed based on the nominal concentration of the test item.

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Remarks:
All validity criteria i.e. immobilization in the controls <=10% and O2 concentrations at the end of the test >=3 mg/L were fulfilled.
Conclusions:
The acute toxicity of a-Ketoglutarate disodium salt (CAS no. 305-72-6) to Daphnia magna was determined in a 48 hour semi-static test according to OECD guideline 202. The median effect concentrations (EC50) of a-Ketoglutarate disodium salt on Daphnia magna were estimated to be >100 mg/l nominal concentration after 24 and 48 h of exposure. The NOEC values were determined to be 100 mg/l nominal concentration after 24 and 48 h of exposure. The results of the test can be considered reliable without restriction.
Executive summary:

The median effect concentration (EC50) and the no-effect concentration (NOEC) of a-Ketoglutarate disodium salt (CAS no. 305-72-6) to Daphnia magna were investigated under semi-static exposure conditions over a period of 48 h, following guideline OECD 202.

The test item a-Ketoglutarate disodium salt is solid, has a high solubility (=511 g/l at pH 7.5 and at 23 °C) and is 99.3% pure. The test media were prepared by directly dissolving the test item in Daphnia medium.

The single investigated nominal concentration was 100 mg/l.

40 individual Daphnia divided into 2 test vessels were exposed to the test item, and 60 Daphnia divided into 3 test vessels were used as blank controls.

The concentrations of a-Ketoglutarate disodium salt in the test medium were determined by HPLC analysis at the beginning, after 24 h in the old and fresh medium, and after 48 h of exposure. These analyses revealed that the concentrations of test item were stable over each 24 h period and remained within 80-120% of the nominal concentration. Therefore, the effective concentrations ECx were assessed based on nominal concentration of the test item.

No significant effects (<=10% immobilization) were observed at 100 mg/l nominal concentration or in the blank controls, neither after 24 h of exposure nor after 48 h.

Therefore, the median effect concentrations (EC50) of a-Ketoglutarate disodium salt (CAS no. 305-72-6) on Daphnia magna after 24 h as well as after 48 h of exposure were estimated to be >100 mg/l nominal concentration.

The NOEC values after 24 h and after 48 h of exposure were both 100 mg/l nominal concentration.

All validity criteria were fulfilled.