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EC number: 268-084-3 | CAS number: 68002-71-1 This substance is identified by SDA Substance Name: C16-C18 trialkyl glyceride and SDA Reporting Number: 19-001-00.
- 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)
Description of key information
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Dose descriptor:
- EC50
- Effect concentration:
- > 1 000 mg/L
Additional information
A study was conducted to evaluate the acute toxicity of the palm kernel stearin toAcartia tonsaunder static conditions. The procedures followed ISO 14669:1999 "Water quality" Part 5: Biological methods Section 5.24: Determination of acute lethal toxicity to marine copepods (Copepoda, Crustacea). Acartia tonsa were exposed towater accommodated fractions prepared fromthe test material at concentrations ranging from 10 to 1,000 mg/L for 48 h and immobility was determined at 24 and 48 h. Under the test conditions, the 48 h EL50 of the test substance was determined to be > 1,000 mg/L (Worden and Sherren, 2004).
A study was conducted to evaluate the acute toxicity of the palm kernel olein toAcartia tonsaunder static conditions. The procedures followed ISO 14669:1999 "Water quality" Part 5: Biological methods Section 5.24: Determination of acute lethal toxicity to marine copepods (Copepoda, Crustacea). Acartia tonsa were exposed towater accomodated fractions prepared fromthe test material at concentrations ranging from 10 to 1,000 mg/L for 48 h and immobility was determined at 24 and 48 h. Under the test conditions, the 48 h EL50 of the test substance was determined to be >1,000 mg/L (Worden and Sherren, 2004).
A study was conducted to evaluate the acute toxicity of the constituent C8 -18, C18 -unsatd. (palm kernel oil) to Acartia tonsa under static conditions. The method followed the guideline ISO 14669:1999 "Water quality" Part 5: Biological methods Section 5.24: Determination of acute lethal toxicity to marine copepods (Copepoda, Crustacea). Acartia tonsa were exposed to water accomodated fractions prepared from the constituent at concentrations ranging from 10 to 1,000 mg/L for 48 h and immobility was determined at 24 and 48 h. Under the test conditions, the 48 h EL50 of the constituent was determined to be >1,000 mg/L (Worden and Sherren, 2004).
A study was conducted to evaluate the acute toxicity of water accommodated fractions (WAFs) or dispersions (in Tween 80) of crude and refined palm oil to Acartia tonsa under static conditions. Acartia tonsa was exposed to crude and refined palm oil at concentrations up to either 3200 (crude oil) or upto 1000 (refined oil) mg/L for 48 h. Based on the results obtained, the 48 h acute toxicity (LC50/LL50) of crude palm oil to Acartia tonsa was considered to be > 3,200 mg/L (WAFs) and > 1,000 mg/L (dispersions). The 48 h acute toxicity (LC50/LL50) of refined palm oil to Acartia tonsa were considered to be > 1,000 mg/L (WAFs) and ca. 1,000 mg/L (dispersions) (Bowmer, 1998).
A study was conducted to evaluate the acute toxicity of crude soybean oil to Acartia tonsa under static conditions. The procedure was based on guidelines issued by ISO 14669, ISO 10253 and GESAMP. Acartia tonsa were exposed to water accomodated fractions (WAF) prepared fromthe test material at concentrations of 0 and 1,000 mg/L and immobility was determined at 0, 24 and 48 h. 3,5 -dichlorophenol was used as a reference substance. Under the test conditions, the 48 h EL50 of crude soybean oil was determined to be > 1,000 mg/L (Worden and Sherren, 2002).
A study was conducted to evaluate the acute toxicity of crude palm oil to Acartia tonsa under static conditions. The procedure was based on guidelines issued by ISO 14669, ISO 10253 and GESAMP. Acartia tonsa were exposed towater accomodated fractions prepared fromthe test material at concentrations of 0 and 1,000 mg/Land immobility was determined at 0, 24 and 48 h. 3,5 -dichlorophenol was used as a reference substance. Under the test conditions, the 48 h EL50 of test substance was determined to be > 1,000 mg/L (Worden and Sherren, 2002).
A study was conducted to evaluate the acute toxicity of "Glycerides C8 -18, C18 -unsatd (coconut oil)" to Acartia tonsa under static conditions. The procedures followed ISO 14669:1999 "Water quality" Part 5: Biological methods Section 5.24: Determination of acute lethal toxicity to marine copepods (Copepoda, Crustacea). Acartia tonsa were exposed towater accommodated fractions prepared fromthe test material at concentrations ranging from 10 to 1,000 mg/L for 48 h and immobility was determined at 24 and 48 h. Based on the results, the 48 h EL50 of the test substance was determined to be between 100 and 1,000 mg/L ((Worden and Sherren, 2004).
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