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EC number: 205-758-8 | CAS number: 150-38-9
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: EEC Guideline XI/681/86, Draft 4: "Prolonged toxicity study with Daphnia magna: Effects on reproduction"
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Samples for analysis were taken in the 1st, the 2nd and the 3rd week of the test. For each concentration the freshly prepared test solution (unstocked) and the corresponding 48 h or 72 h old test solution (stocked with daphnids) were analyzed.
- Vehicle:
- no
- Details on test solutions:
- At the beginning of the test and before changing the test solutions, a stock solution of the test substance was freshly prepared. A defined amount of the substance was weighed out and suspended directly in the test medium by stirring (about 10 min at 22 ± 1 °C). The nominal concentrations of the stock solutions were 100 mg/L. By dilution of the stock solutions with test medium, the nominal test concentrations were prepared.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Species: Daphnia magna STRAUSS
Supplier: Institut National de Recherche Chimique Appliquée, France, 1978
Culture: The daphnids are cultured under standard conditions in the Laboratory for Experimental Ecology of BASF AG, Ludwigshafen, Germany - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 21 d
- Hardness:
- Total hardness: 2.20 - 3.20 mmol/L
- Test temperature:
- 19.9 - 21.7 °C
- pH:
- 7.5-8.5
- Dissolved oxygen:
- Oxygen content: 8.0 - 9.6 mg/L
- Nominal and measured concentrations:
- Test concentrations (nominal): 100; 50.0; 25.0; 12.5; 6.25; 3.13 and 1.56 mg/L (Dilution factor: 2)
- Details on test conditions:
- TEST PROCEDURE
- Semistatic procedure: Change of test solution three times a week.
- Test water: synthetic M4-medium
Alkalinity up to pH 4.3: 0.80 - 1.00 mmol/L
Molar ratio Ca:Mg: about 4 : 1
Conductivity: 550 - 650 µS/cm
- Number of animals/vessel: 1
- Number of replicates/concentration: 10
- Number of replicates/control: 10
- Age of the animals at the start of the test: 2 - 24 h
- Age of stock animals: 2 - 4 weeks
- Light: Artificial light, OSRAM L58 W31 warm white day : night-rhythm = 16 : 8 hours
- Removal of young from test beakers and counting: daily
- Check of the study and recording (mortality, hatching of young): daily
- Feeding: daily
- Measurement of temperature: Continuously in an extra vessel
- Measurement of pH and oxygen: At the start of the test and at each change of test solution in the 48 or 72-hour-old solution in one parallel at each concentration - Key result
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 25 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- LOEC
- Effect conc.:
- 50 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- other: LC0
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Reported statistics and error estimates:
- For the statistical evaluation of the LOEC and NOEC Duncan's new multiple range test was used.
- Validity criteria fulfilled:
- yes
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- Refer to the Analogue Approach Justification document provided in Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 25 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- LOEC
- Effect conc.:
- 50 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- other: LC0
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Validity criteria fulfilled:
- yes
Referenceopen allclose all
Analytically found relative minimum and maximum concentrations of the test substance in the test solutions at different times of the test (with and without daphnids). The values are given in percent of the nominal concentrations:
Time [h] |
Stocked with daphnids |
Minimum [%] |
Maximum [%] |
0 |
No |
80.8 |
166.7 |
48/72 |
No |
92.8 |
166.7 |
48/72 |
Yes |
95.2 |
173.1 |
M4-water caused a background value of about 1 mg/L "Trilon BD". Regarding to this and to the precision of the analytical method, most concentrations found corresponded to the expected values.
Validity criteria: In the control:
- The mortality of parent animals up to the end of the test was <= 10 %.
- The mean number of living young per parent animal that survived the test was >= 60.
- The coefficient of variation for the mean number of living young per parent animal that survived the test was <= 25 %.
- The NOEC of the control substance 3,4-dichloroaniline was 2.5 µg/L, the LOEC was 10 µg/L and LC0 was > 10 µg/L.
The validity criteria were fulfilled by the test.
Control:
In the control the first young were observed at day 7. In the highest concentration tested, at which the daphnids produced young (100 mg/L), the first young were observed at day 13.
Description of key information
NOEC (21 d): 25 mg/L (EEC Guideline XI/681/86, Draft 4); read-across
Key value for chemical safety assessment
Additional information
Since no studies investigating the long-term toxicity trisodium hydrogen EDTA (CAS 150-38-9) to aquatic invertebrates are available, in accordance to Regulation (EC) No 1907/2006 Annex XI, 1.5 a read-across to a structurally related EDTA species was conducted. This read-across is justified in detail in the overall summary (IUCLID Section 6.1) and within the analogue justification in IUCLID Section 13.
The study was performed according to EEC Guideline XI/681/86, Draft 4 (GLP) which is considered to be equivalent or similar to OECD 211. The source substance disodium dihydrogen EDTA (CAS 139-33-3) was used for testing. Daphnia magna was exposed to concentrations of 1.56 to 100 mg/L in synthetic M4-medium under semi-static conditions. The actual exposure concentrations were measured in each week of the test (freshly prepared solutions and 48 h or 72 h old solutions) and approximately corresponded to the nominal values (taking into account the background level of Na2H2-EDTA in the test medium). Thus, the effect concentrations were based on the nominal concentrations. In the test medium the pH-value ranged between 7.3 and 8.5 and the oxygen content between 8.0 and 9.6 mg/L. The total hardness of the medium was 220.2 - 320.3 mg CaCO3/L. In the control the first rising generation was observed at day 7. In the highest concentration tested, the Daphnids produced young (100 mg/L) at day 13. After 21 d a NOEC of 25 mg/L was derived based on reproduction.
In conclusion, the long-term toxicity of trisodium hydrogen EDTA (CAS 150-38-9) to aquatic invertebrates is considered to be in the same range.
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