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EC number: 701-284-5 | CAS number: 2137881-70-8
- 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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Justification for type of information:
- It is considered appropriate to address the data requirements for reaction mass of 2,2-bis(formyloxymethyl)propane-1,3-diyl diformate and formic acid by read-across to the available studies on structurally similar substances.
Reaction mass of 2,2-bis(formyloxymethyl)propane-1,3-diyl diformate and formic acid is comprised of formic acid (free) up to 59%, propylidynetrimethanol (trimethylolpropane, TMP) up to 35%, and pentaerythritol up to 19.6%.
Long-term aquatic invertebrate toxicity studies are available on formic acid, propylidynetrimethanol (trimethylolpropane, TMP), and pentaerythritol. The data requirements for reaction mass of 2,2-bis(formyloxymethyl)propane-1,3-diyl diformate and formic acid are addressed by read-across to formic acid, propylidynetrimethanol (TMP) and pentaerythritol. - Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Specific details on test material used for the study:
- Formic acid, propylidynetrimethanol (trimethylolpropane, TMP), and pentaerythritol are being used as a read across for 2,2-bis(formyloxymethyl)propane-1,3-diyl diformate and formic acid.
- Key result
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- reproduction
- Remarks on result:
- other: Key data from formic acid study
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- > 1 000 mg/L
- Remarks on result:
- other: Key data from TMP study
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- not specified
- Basis for effect:
- reproduction
- Remarks on result:
- other: Key data from pentaerythritol study
- Details on results:
- The key data from long-term aquatic invertebrate toxicity studies on formic acid, propylidynetrimethanol (trimethylolpropane, TMP), and pentaerythritol are used for weight of evidence read across to reaction mass of 2,2-bis(formyloxymethyl)propane-1,3-diyl diformate and formic acid.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The long-term toxicity of the target substance, reaction mass of 2,2-bis(formyloxymethyl)propane-1,3-diyl diformate and formic acid, to aquatic invertebrates was estimated to be 21 d NOEC = ≥100 mg/L, based on a worst case read-across study on formic acid exposure to D. magna.
- Executive summary:
Long-term studies are available on the chronic toxicity to Daphnia for the read-across substances formic acid, propylidynetrimethanol (trimethylolpropane, TMP), and pentaerythritol:
A long-term study exists for the read-across substance, formic acid. To determine chronic effects of formic acid to aquatic invertebrates, a semi-static GLP study according to OECD guideline 211 using Daphnia magna was performed. The calculated NOEC value (21 d) in this study was 100 mg/L, related to the nominal concentrations which were verified analytically (BASF SE, 2007).
A static 21 d test was performed with TMP on D. magna which followed an OECD Guideline not further specified, which determined a NOEC of >1000 mg/L. The study was performed by the Japanese Environmental Agency according to an OECD-Guideline, and is considered to be acceptable.
Four replicates, each containing 10 female D. magna, were exposed to a series of concentrations of pentaerythritol in a semi-static for a 21 d period. There was no adult mortality during the study, therefore the 21 d LC50 was observed to be >1000 mg/L (the highest nominal exposure concentration tested). There were no significant differences in the number of juveniles produced per female in the control and test treatments during the study. Therefore, the no-observed effect concentration based on reproduction was 1000 mg/L (the highest nominal exposure concentration tested).
Reference
Description of key information
The 21 day NOEC for reproduction was found to be >100 mg/l.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 100 mg/L
Additional information
Long-term studies are available on the chronic toxicity to Daphnia for the read-across substances formic acid, propylidynetrimethanol (trimethylolpropane, TMP) and pentaerythritol:
A long-term study exists for the read-across substance, formic acid. To determine chronic effects of formic acid to aquatic invertebrates, a semi-static GLP study according to OECD guideline 211 using Daphnia magna was performed. The calculated NOEC value (21 d) in this study was 100 mg/L, related to the nominal concentrations which were verified analytically (BASF SE 2007).
A static 21 d test was performed with TMP on D. magna by following a OECD Guideline not further specified.
A NOEC > 1000 mg/L was determined. Being performed by EA Japan according to a OECD-Guideline, the study is considered to be acceptable.
Four replicates, each containing 10 female D. magna, were exposed to a series of concentrations of pentaerythritol in a semi-static for a 21 d period. There was no adult mortality during the study, therefore the 21 d LC50 was observed to be >1000 mg/L (the highest nominal exposure concentration tested). There were no significant differences in the number of juveniles produced per female in the control and test treatments during the study. Therefore, the no-observed effect concentration based on reproduction was 1000 mg/L (the highest nominal exposure concentration tested).
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