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Diss Factsheets
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EC number: 700-751-0 | CAS number: -
- 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
Water solubility
Administrative data
Link to relevant study record(s)
Description of key information
The water solubility of Ca-/Mg-salt of Fumarated Tall Oil Rosin was determined at 20°C according to OECD TG 105 using the flask method.
At an initial weight of 10 g /L and 0.1 g/L, a water solubility of 0.154 to 0.442 g/L test item and < 0.0027 g/L test item, respectively was observed.
Key value for chemical safety assessment
- Water solubility:
- 442 mg/L
- at the temperature of:
- 20 °C
Additional information
As the test item is a UVCB substance, the test design had to be adapted. The flask method was chosen to determine the water solubility of Ca/Mg-salt of fumarated Tall Oil Rosin, as the elution method is not suitable for UVCB substances.
For a complex substance the water solubility fraction strongly depends on the amount of test substance added. Therefore, two loading rates (0.1 g/L and 10 g/L) were tested resulting in a significant higher water solubilty at an initial weighing of 10 g/L compared to concentrations found at initial concentrations of 0.1 g/L. As the substance consists of components with a low as well as a high water solubility, higher loading rates might thus result in the dissolution of higher portions of soluble components. Experiments were evaluated on the basis of the total organic carbon (TOC) content of the aqueous phase (sum parameter), as the quantification based on individual components is not feasible.
Normally, the flasks are stirred up to 72 h to achieve equilibrium between the dissolved and undissolved fraction shown by a constant aqueous concentration throughout the test period. This could not be observed as the concentration found in the water phase decreased after 48 h.
To determine aqueous concentrations after distinct periods of stirring (24 h, 48 h and 72 h), individual flasks were prepared. As the test item was coarse grained having a heterogeneous particle size distribution, each flask might contain grains of different sizes. The dissolution behavior might thus be influenced by the surface area of the pieces included explaining the decreasing aqueous concentration after 48 h.
Concluding, the variable concentrations observed result from the complex substance composition (presence of good soluble components besides poorly soluble ones) as well as the heterogeneous particle size distribution of the sample. Even so, the study was scored as valid for assessment providing information about the order of magnitude in which the substance will be dissolved in an aqueous medium.
It is assumed that the highest value reported represents the worst case, this was taken as key value.
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