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EC number: 944-170-2 | CAS number: -
- Life Cycle description
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- Endpoint summary
- Appearance / physical state / colour
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- Density
- Particle size distribution (Granulometry)
- Vapour pressure
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- Endpoint summary
- Stability
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- 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
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- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
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- Acute Toxicity
- Irritation / corrosion
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- Genetic toxicity
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- Specific investigations
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- Additional toxicological data

Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 12.05.1992-04.06.1992
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- without analytical monitoring
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- part I, 24h EC50 Acute Immobilization Test (1984)
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 1.9 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CL: 1.37 - 2.69 mg a.i./L
- Reported statistics and error estimates:
- The EC50 value was calculated using the Litchfield Wilcoxon method.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The acute toxicity of Coco AAPB to Daphnia magna was investigated in a study conducted according to OECD guideline 202. The 48 h EC50 was determined to be ca. 1.9 mg a.i./L nominal.
- Executive summary:
The acute toxicity of Coco AAPB to Daphnia magna was investigated in a study conducted according to OECD TG 202 / I under static conditions. Daphnia magna was exposed to 6 nominal concentrations ranging from 0.5 to 16 mg product/L. A 48 h LC50 of ca. 1.9 mg a.i/L nominal was determined based on an active matter content of 30%.
This study is regarded as reliable with restrictions.
Results Synopsis
Test Organism/Age (e.g. 1stinstar): Daphnia magna/<24 h
Test Type: Static
48 h EC50: ca. 1.9 mg a.i./L; 95% C.I.: 1.37-2.69 mg a.i./L (active matter assumed: 30%; values refer to nominal concentrations)
Endpoint(s) Effected: Immobilization
Reference
RESULTS: EXPOSED
- Nominal/measured concentrations: nominal
- Effect data (Immobilization):
concentration number of number of animals
(mg/l) animals immobilized after 48h
0.5 20 0
1 40 2
2 40 3
4 20 6
8 20 9
16 20 20
Based on the number of immobilized animals after 48h, the EC50 value was calculated using the method of Litchfield and Wilcoxon.
48 h EC50: 6.4 mg product/L
with 95% confidence limit of 4.57 - 8.96 mg product/L
Assuming a content of 30% active substance:
48 h EC50: ca. 1.9 mg active substance/L
with confidence limit of 1.37 - 2.69 mg a.i./L
Description of key information
48 h EC50 = 1.9 mg a. i./L (nominal), OECD TG 202 / part I (1984) static, Daphnia magna, GLP, RL2; read-across: C8-18 and C18 unsatd. AAPB
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 1.9 mg/L
Additional information
No experimental data are available for the target substance C8-10 Alkylamidopropyl betaine. However, short-term toxicity studies with aquatic invertebrates are available for the source substances Formamidopropylbetaine, C8-18 AAPB and C8-18 and C18 unsatd. AAPB. A justification for read-across is given in the Endpoint summary “Aquatic Toxicity”.
The acute toxicity of C8-18 and C18 unsatd. AAPB to Daphnia magna was investigated in a study conducted according to OECD TG 202 / part I (1984) under static conditions. Daphnia magna was exposed to 6 nominal concentrations ranging from 0.5 to 16 mg product/L. A 48 h LC50 of ca. 1.9 mg a.i/L (nominal) was determined based on an active matter content of 30%.
The 48 hr-acute toxicity of C8-18 AAPB (30% active matter) to Daphnia magna was investigated in a study conducted according to OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test) and EU Method C.2 (Acute Toxicity for Daphnia) under static conditions. Daphnids were exposed to control and test chemical at nominal concentrations of 6.25; 12.5; 25; 50; 100 mg product/L for 48 hr. The test material concentrations were analysed via UV absorption at 485 nm. The C8-18 AAPB concentrations were >80% (exception: 72.2% at the start in the 6.25 mg product/L group). The 48 h EC50 was determined to be 6.5 mg a.i./L based on nominal concentrations.
The acute toxicity of Formamidopropylbetaine to Daphnia magna was investigated in a study conducted according to OECD Guideline 202. The substance did not induce acute immobilisation of Daphnia magna at 100 mg/L after 48 hours of exposure. The 48h-EC50 was > 100 mg/L based on analytically confirmed nominal exposure concentrations.
Conclusion
For freshwater invertebrates (Daphnia magna) the lowest 48 h EC50 was determined to be 1.9 mg a. i./L (nominal).
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