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EC number: 244-599-9 | CAS number: 21829-50-5
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
The 48-h LC50 value for citric acid in fish (golden orfe) is 440 mg/L, the 96-h LC50 value for monoethanolamine is 349 mg/L. After correction for molecular weight the effect concentrations for tris[(2-hydroxyethyl)ammonium] citrate are 860 and 2142 mg/L, respectively. The lowest value of 860 mg/L will be used in the assessment.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 860 mg/L
Additional information
Short-term studies with fish are not available for tris[(2-hydroxyethyl)ammonium] citrate. Tris[(2-hydroxyethyl)ammonium] citrate is the neutral salt of monoethanolamine and citric acid. Monoethanolamine and citric acid are the starting materials for the synthesis of tris[(2-hydroxyethyl)ammonium] citrate, and the only difference is that in tris[(2-hydroxyethyl)ammonium] citrate the substances are present in their ionic forms as a monoethanolamine cation and a citrate anion. It is expected that the ecotoxicological properties of tris[(2-hydroxyethyl)ammonium] citrate shall be governed by the properties of monoethanolamine and citric acid (for more details see reporting format for the analogue approach in Appendix A.2).
For monoethanolamine a GLP-compliant Directive 92/69/EEC, C.1. guideline study with carp (Cyprinus carpio) is available (Huels, 1997b). Fish (10/dose) were exposed to nominal concentrations of 3 to 1,000 mg/L under semi-static conditions for 96 hours, the test concentrations were analytically verified and were within 80% of nominal concentrations. None of the controls or fish exposed to 90 mg/L died. One fish exposed to 150 mg/L died between 72 and 96 hours. Two fish exposed to 280 mg/L died within 72 hours. All fish exposed to 500 and 900 mg/L were dead by 48 and 24 hours, respectively. A 96-h LC50 value 349 mg/L is reported. A safety factor need not to be applied to this value. Instead, the effect concentration is corrected for molecular weight which leads to an effect concentration of 2142 mg/L for tris[(2-hydroxyethyl)ammonium] citrate.
For citric acid a non-GLP study is available for golden orfe (Leucidus idus melanotus) which was performed in a method equivalent to OECD guideline 203 (Juhnke and Lüdemann, 1978). In this study, fish (10/dose) were exposed to citric acid in a static system. Little further information on test conditions and design is available. A 48-h LC50 value of 440 mg/L is reported. A safety factor need not to be applied to this value. Instead, the effect concentration is corrected for molecular weight which leads to an effect concentration for tris[(2-hydroxyethyl)ammonium] citrate of 860 mg/L.
The lowest effect concentration of 860 mg/L will be used in the assessment.
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