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EC number: 825-814-0 | CAS number: 222721-94-0
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- Please see Analogue Approach
- Reason / purpose for cross-reference:
- read-across source
- Analytical monitoring:
- yes
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EL10
- Effect conc.:
- > 100 other: % satured solution
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- loading rate
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- loading rate WAF
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- >= 100 other: % saturated solution
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- loading rate
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- > 50 other: % saturated solution
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- loading rate
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- loading rate WAF
- Basis for effect:
- other: yield inhibition
- Conclusions:
- In this study static algae test according to OECD-guideline 201 1,2,3-Propanetricarboxylic acid, 2-Hydroxy-, tris(C12-C13-branched-alkyl)ester was found to slightly inhibit the growth of the freshwater green alga Pseudokirchneriella subcapitata after 72 hours. The NOEC-values for inhibition of both growth rate and yield after 72 hours were 50.0 % of the saturated solution. The EC50-values for inhibition of both growth rate (ErC50) and yield (EyC50) after 72 hours were > 100 % of the saturated solution (100 mg/L nominal loading rate WAF).
The growth rate inhibition at 100 % saturated solution was found to be statistical significant at 3 % inhibition compared to control. Due to this low inhibitory effect (< 10 %, biological significance) it may be justified to assume this effect as unspecific.
No further effects are expected at higher concentrations of nominal 100 mg/L due to the calculated water solubility of ≤ 0.739 ng/L. - Executive summary:
The toxicity of 1,2,3-Propanetricarboxylic acid, 2-Hydroxy-, tris(C12-C13-branched-alkyl)ester to the unicellular freshwater green alga Pseudokirchneriella subcapitata was determined according to the principles of OECD 201 and Council Regulation (EC) No. 761/2009 Method C.3. The aim of the study was the determination of NOEC, LOEC, EC10- , EC20- and EC50-values of growth rate and yield over a period of 72 hours. The study was conducted under static conditions with an initial cell density of 6153 cells/mL. A saturated solution of 100 mg/L was prepared with dilution water and stirred for 48 hours. Then undissolved particles were removed by membrane filtration (membrane filter 0.2 µm, RC, MACHEREY-NAGEL). Five concentrations were tested in a geometrical series with a dilution factor of 2: 6.25 - 12.5 - 2.50 - 50.0 - 100 %. Three replicates were tested for each test item concentration and six replicates for the control. The environmental conditions were within the acceptable limits. The test media were clear throughout the test period. The concentrations of the test item 1,2,3 -Propanetricarboxylic acid, 2 -Hydroxy-, tris(C12 -C13 -branched-alkyl)ester in all test concentrations and the control were analytically verified by LC-MS/MS at the start and the end of exposure. The saturated solution with a nominal concentration of 100 mg/L was diluted to prepare different concentrations. To account for the low calculated water solubility of the substance, all effect values given are based on nominal test item concentrations.
Only slight effects of the test item 1,2,3-Propanetricarboxylic acid, 2-Hydroxy-, tris(C12-C13-branched-alkyl)ester on the green alga Pseudokirchneriella subcapitata in terms of inhibition of growth or yield was found up to the 100 % saturated solution. The growth rate inhibition at 100 % saturated solution was found to be statistical significant at 3 % inhibition compared to control. Due to this low inhibitory effect (10 %, biological significance) it may be justified to assume this effect as unspecific. No further effects are expected at higher concentrations of nominal 100 mg/L, due to the calculated water solubility of ≤ 0.739 ng/L.
Reference
Description of key information
In an algae test according to OECD-guideline 201 with the similar substance 1,2,3 -Propanetricarboxylic acid, 2 -Hydroxy-, tris(C12 -C13 -branched-alkyl)ester the test substance was found to slightly inhibit the growth of the freshwater green alga Pseudokirchneriella subcapitata after 72 hours. The NOEC-values for inhibition of both growth rate and yield after 72 hours were 50.0 % of the saturated solution. The EC50 -values for inhibition of both growth rate (ErC50) and yield (EyC50) after 72 hours were > 100 % of the saturated solution (100 mg/L nominal loading rate WAF). Also the source substance Tri (hexyl, octyl, decyl) citrate was not toxic up to the limit of water solubility.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 100 mg/L
Additional information
The toxicity of the similar substance 1,2,3-Propanetricarboxylic acid, 2-Hydroxy-, tris(C12-C13-branched-alkyl)ester to the unicellular freshwater green alga Pseudokirchneriella subcapitata was determined according to the principles of OECD 201 and Council Regulation (EC) No. 761/2009 Method C.3. The aim of the study was the determination of NOEC, LOEC, EC10- , EC20- and EC50-values of growth rate and yield over a period of 72 hours. The study was conducted under static conditions with an initial cell density of 6153 cells/mL. A saturated solution of 100 mg/L was prepared with dilution water and stirred for 48 hours. Then undissolved particles were removed by membrane filtration (membrane filter 0.2 µm, RC, MACHEREY-NAGEL). Five concentrations were tested in a geometrical series with a dilution factor of 2: 6.25 - 12.5 - 2.50 - 50.0 - 100 %. Three replicates were tested for each test item concentration and six replicates for the control. The environmental conditions were within the acceptable limits. The test media were clear throughout the test period. The concentrations of the test item 1,2,3 -Propanetricarboxylic acid, 2 -Hydroxy-, tris(C12 -C13 -branched-alkyl)ester in all test concentrations and the control were analytically verified by LC-MS/MS at the start and the end of exposure. To account for the low calculated water solubility of the substance, all effect values given are based on nominal test item concentrations.
The influence of the source substance 1, Tri (hexyl, octyl, decyl) citrate, on the growth of the green algal species Scenedesmus subspicatus CHODAT was investigated in a 72 -hour static test according to the OECD Guideline No. 201, adopted June 7, 1984. The test was performed in compliance with GLP. Due to the low water solubility of the test substance a filtrate of a supersaturated stock suspension of nominal 100 mg/L was tested. Thus, no concentrations above the solubility limit of the test substance in the used test water were tested. Also due to the low water solubility no analytical verification could be done in the present test. Therefore, the biological results could not be related to a specific concentration of the test substance but only to the water solubility limit in the test medium.
The 72-hour NOEC was determined to be at least up to the solubility limit of the test substance. The NOEC might even be higher than this concentration, but concentrations in excess of the solubility limit had not been tested. The 72-hour LOEC and the 72-hour EC50 were clearly higher than the solubility limit.
It is expected that the same is valid for the substance 1,2,3-Propanetricarboxylic acid, 2-hydroxy-, tri-C14-15-alkyl esters.
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