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Diss Factsheets
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EC number: 204-815-4 | CAS number: 126-97-6
- 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:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Justification for type of information:
- REPORTING FORMAT FOR THE CATEGORY APPROACH
1. HYPOTHESIS FOR THE CATEGORY APPROACH
This scenario covers the category approach for which the hypothesis is based on transformation to a common compound. For the REACH information requirement under consideration, the effects obtained in studies conducted with different source substances are used to predict the effects that would be observed in a study with the target substance if it were to be conducted. The same type of effect is observed for the different source substances; this may include absence of effects for every member of the category. No relevant differences in strengths of effect are observed for several source substances.
There are no relevant variations in properties among source substances and the same potency is predicted for all target substances. This corresponds to Scenario 5 of the RAAF (ECHA, 2017). The substances ATG, MEATG, KTG, CaTG, and NaTG are different inorganic salts of a common acid, thioglycolic acid (TGA; synonym: 2-mercaptoacetic acid). They dissociate rapidly in aqueous media to the common thioglycolate anion and to their different counter ions. The water solubility of all category members is high.
This approach serves to use existing data on aquatic toxicity endpoints for substances in this category.
It can be predicted with high confidence that the target substances will display the same mode of action and lead to the same type and strength of effects as observed with the source substances.
2. CATEGORY APPROACH JUSTIFICATION
For details, refer to Justification for read-across attached to Iuclid section 13 - Reason / purpose for cross-reference:
- read-across: supporting information
- Key result
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 5.3 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- other: read-across, molecular weigth correction
- Basis for effect:
- reproduction
- Conclusions:
- After molecular weight correction, the 21 d NOEC for MeaTG is 5.3 mg/L, and the LOEC is 12.7 mg/L.
Reference
Description of key information
21-Day NOEC = 5.3 mg/L (OECD TG 211, Daphnia magna, RL2, GLP; read-across from TGA, molecular weight correction)
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Dose descriptor:
- NOEC
- Effect concentration:
- 5.3 mg/L
Additional information
No experimental data on long-term toxicity to aquatic invertebrates is available for the target substance MeaTG. However, a study was conducted with teh source substance TGA. A category justification is attached to Iuclid section 13.
A Daphnia magna reproduction test was conducted according to OECD Guideline 211 (Draft, April 1997). Daphnids, aged less 24 hours at the start of the test, were exposed to thioglycolic acid at nominal concentrations of 0.0 (control), 5.4, 8.6, 13.7, 21.9, and 35.0 mg/L; corresponding to measured concentrations of 0.0, 1.2, 1.7, 2.7, 6.5, and 24.2 mg/L) for 21 days under semi-static conditions (daily renewal). At the end of the test, the total number of living offspring produced was assessed. Because the measured concentrations were outside of ± 20% of the nominal concentrations, the time-weighted average of the measured concentration was used to calculate the test results.
The mortality rate of the parent Daphnia magna in the control was 10% at the end of exposure, meeting the test acceptance criteria of 20% or less.
In the concentrations, as the test substance concentration increased, the number of deaths and mortality rate of parent Daphnia magna increased at the end of exposure, and in the concentration of 1.7 mg/L, the mortality rate of parent Daphnia magna was 30%, and it was 100% in the maximum concentration (24.2 mg/L)
The first hatching date for the parent Daphnia magna in the control was 10 to 11 days after the start of exposure. In the concentration of 1.7 mg/L, the first hatching date for the parent Daphnia magna was 10 to 14 days after the start of exposure, and in the highest concentration (24.2 mg/L), no offspring of the parent Daphnia magna was found.
The mean cumulative number of litter per parent Daphnia magna during the 21-day control zone was 67.8, meeting the test acceptance criteria of 60 or more.
The mean cumulative number of offspring per parent Daphnia magna during the 21-day concentrations was 74.4 animals in the lowest concentration (1.7 mg/L), and all of the parent Daphnia magna died in the highest concentration (24.2 mg/L) at 21 days of exposure.
No dormant eggs, etc. occurred in the control or any of the concentration.
Results:
21-Day No Observed Effect Concentration (NOECr) = 2.7 mg/L
21-Day Lowest Observed Effect Concentration (LOECr) = 6.5 mg/L
21-Day 50% Lethal Concentration of Parent Daphnia magna (LC50) = 5.7 mg/L (95% confidence interval: 3.4 mg/L - 11.2 mg/L)
21-Day 50% Reproductive Inhibition Concentration (ErC50) = 4.1 mg/L (95% confidence interval: 3.6 mg/L - 4.8 mg/L)
Conclusion
After molecular weight correction, the 21 d NOEC for MeaTG is 5.3 mg/L, and the LOEC is 12.7 mg/L.
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