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EC number: 617-084-5 | CAS number: 80474-45-9
- 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
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:
- 20th May 2003 - 3rd April 2004
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- yes
- Specific details on test material used for the study:
- Test Substance:
Test substance name: Thio-Acid Propionate
Sponsor batch number: H030714
Purity: 100%
Description: White/off-white crystalline solid
Storage: 10-20°C (avoid prolonged storage at elevated temperatures above 20°C). Avoid direct sunlight.
Expiry date: Not stated
Water solubility: <10g/l at 20°C
Date received: 26 April 2003 - Details on sampling:
- Juvenile Daphnia magna, (less than 24 hours old), were taken from a laboratory culture maintained at Covance Laboratories Ltd. The culture was originally obtained from Sheffield University, Sheffield, UK.
The water in each culture was renewed weekly. All cultures, prior to and during toxicity tests, were maintained under fluorescent lighting on a 16-hour light: 8-hour dark photo-period. - Details on test solutions:
- At the start of the exposure period, the prepared test media appeared as a colourless solution. After 48 hours, the appearance of the test media was unchanged.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- The daphnia magna were cultured in 600mL glass beakers containing 500mL of standard hard water. Each culture vessel and its contents were referred to as a "culture". New cultures were started with juvenile Daphnia magna (less than 24 hours old), at a density of approximately 20 animals per litre. Each of the cultures was fed daily with a concentrated suspension of Chlorella culgaris (a unicellular green algae). The Chorewlla vulgaris was obtained from a fermenter-based culture, grown under semi-axenic conditions at Covance Laboratories Ltd in accordance with Covance's Standard Operating Procedures. A seaweed extract (Ascophyllum nodosum) prepared in accordance with Covance's Standard Operating Procedures was added once a week (at medium renewal) to each culture as a dietary supplement.
- Test type:
- static
- Water media type:
- other: ASTM water
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- After 24 and 48 hours, the numbers of immobilised Daphnia magna were recorded. The Daphnia magna were considered immobile if, when the contents of the test vessel were agitated, active swimming was not observed during a 15-second period of observation.
- Hardness:
- Total hardness as CaCO3 (mg/L): 163
- Test temperature:
- 20-21.1°C
- pH:
- 7.4-7.7
- Dissolved oxygen:
- Dissolved oxygen (% air saturated value): 85-97
- Nominal and measured concentrations:
- The definitive test was conducted at the nominal Thio-Acid propionate exposure concentrations of 6.3, 12.5, 25, 50 and 100mg/L.
- Key result
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Conc. based on:
- test mat.
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Conc. based on:
- test mat.
- Details on results:
- At the start of the exposure period, the prepared test media appeared as a colourless solution. After 48 hours, the appearance of the test media was unchanged.
Toxicity to Daphnia Magna:
At 24 hours, immobile Daphnia magna were observed in the control, 6.3, 25, 50 and 100 mg/L treatments. In the 12.5mg/L treatment, there were 3 Daphnia magna recorded immobile out of 20 exposed, corresponding to 15% immobility.
At 48 hours, no immobile Daphnia magna were observed in the control, 50 and 100 mg/L treaments. In the 6.3, 12.5 and 25mg/L treatments there were 1, 2 and 3 immobile Daphnia magna recorded respectively, corresponding to 5, 10 and 15% immobility respectively.
As there was no signficant immobility observed during the definitive test, the 24 and 48 hour EC50 values, and the corresponding no observed effect concentration (NOEC) for Daphnia magna exposed to Thio-Acid Propionate could not be determined. Therefore the 24 and 48 hour EC50 values are considered to be >100 mg/L, the highest nominal exposure concentration in the definitive test. - Validity criteria fulfilled:
- yes
- Conclusions:
- As there was no significant immobility observed during the definitive test, the 24 and 48 hour EC50 values, and the corresponding no observed effect concentration (NOEC) for Daphnia magna exposed to Thio-Acid Propionate could not be determined. Therefore the 24 and 48 hour EC50 values are considered to be >100 mg/L, the highest nominal exposure concentration in the definitive test.
- Executive summary:
The acute toxicity of Thio-Acid Prionate to Daphnia magna was determined at 20 +/- 2°C in a 48-hour static (without renewal of the test media) definitive test.
The definitive test was conducted at the nominal Thio-Acid propionate exposure concentrations of 6.3, 12.5, 25, 50 and 100mg/L. The range of concentrations was selected based on the results of a range finding limit test, which is not reported.
Four replicate vessels were prepared at each concentration with each vessel containing five juvenile Daphnia magna.
In the definitive test, the 100mg/L test media was prepared by adding 0.1048g to a 1 litre volumetric flask and making up to volume with ASTM. The flask contents were treated with ultrasound for 30 minutes and stirred for approximately 1 hour on a magnetic stirrer. The remaining exposure concentrations were prepared by serial dilution of the 100mg/L test medium.
Due to the low numbers of Daphnia magna immobilised during the test, a 48 hour EC50toxicity value could not be calculated. Therefore, the 48 hour EC50value and corresponding no observed effect concentration (NOEC) are assumed to be >100mg/L for Thio-Acid Propionate, the hightest nominal exposure concentration tested.
Reference
Observations of Daphnia magna after 24 hours exposure to Thio-Acid Propionate:
Nominal Thio-Acid Propionate concentration (mg/L) | Number of Daphnia magna | Mobile Daphnia (Bottom) | Mobile Daphnia (Surface) | Immobile Daphnia (Bottom) | Immobile Daphnia (Surface) |
Control | 20 | 20 | - | - | - |
6.3 | 20 | 20 | - | - | - |
12.5 | 20 | 17 | - | 3 | - |
25 | 20 | 20 | - | - | - |
50 | 20 | 20 | - | - | - |
100 | 20 | 20 | - | - | - |
Observations of Daphnia magna after 48 hours exposure to Thio-Acid Propionate:
Nominal Thio-Acid Propionate concentration (mg/L) | Number of Daphnia magna | Mobile Daphnia (Bottom) | Mobile Daphnia (Surface) | Immobile Daphnia (Bottom) | Immobile Daphnia (Surface) |
Control | 20 | 20 | - | - | - |
6.3 | 20 | 19 | - | 1 | - |
12.5 | 20 | 18 | - | 2 | - |
25 | 20 | 17 | - | 3 | - |
50 | 20 | 20 | - | - | - |
100 | 20 | 20 | - | - | - |
Description of key information
The acute toxicity of Thio-Acid Prionate to Daphnia magna was determined at 20 +/- 2°C in a 48-hour static (without renewal of the test media) definitive test.
The definitive test was conducted at the nominal Thio-Acid propionate exposure concentrations of 6.3, 12.5, 25, 50 and 100mg/L. The range of concentrations was selected based on the results of a range finding limit test, which is not reported.
Four replicate vessels were prepared at each concentration with each vessel containing five juvenile Daphnia magna.
In the definitive test, the 100mg/L test media was prepared by adding 0.1048g to a 1 litre volumetric flask and making up to volume with ASTM. The flask contents were treated with ultrasound for 30 minutes and stirred for approximately 1 hour on a magnetic stirrer. The remaining exposure concentrations were prepared by serial dilution of the 100mg/L test medium.
Due to the low numbers of Daphnia magna immobilised during the test, a 48 hour EC50toxicity value could not be calculated. Therefore, the 48 hour EC50value and corresponding no observed effect concentration (NOEC) are assumed to be >100mg/L for Thio-Acid Propionate, the hightest nominal exposure concentration tested.
Key value for chemical safety assessment
Additional information
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