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Diss Factsheets
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EC number: 701-236-3 | 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
Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown but no further hazard information necessary as no exposure expected
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown but no further hazard information necessary as no exposure expected
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown but no further hazard information necessary as no exposure expected
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown but no further hazard information necessary as no exposure expected
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2.83 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 300
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 849 mg/kg bw/day
- AF for dose response relationship:
- 1
- Justification:
- default AF
- AF for differences in duration of exposure:
- 6
- Justification:
- sub-acute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- default for rat
- AF for other interspecies differences:
- 2.5
- Justification:
- default for remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- default for workers
- AF for the quality of the whole database:
- 1
- Justification:
- default AF
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - workers
Acute Toxicity
A DNEL for acute toxicity need only be derived if an acute hazard leading to classification for acute toxicity (e. g. under CLP[A1]) has been identified and there is a potential for high peak exposures. If no hazard has been identified, then a DNEL for acute toxicity is unnecessary as the long-term DNEL will be sufficient to ensure that adverse effects do not occur. Distilled tall oil, magnesium salts are not classified for acute toxicity and are not irritant (eye, skin or respiratory tract) and therefore no acute DNELs (systemic or local) have been calculated.
Long-term Systemic Toxicity
Distilled tall oil, magnesium salts is a complex reaction product formed by reacting magnesium hydroxide with distilled tall oil. It has the generic structure RCOO—Mg—OOCR, with the R groups being derived from the distilled tall oil. Distilled tall oil is a UVCB substance derived from natural sources and typical analysis shows it comprises a mixture of unsaturated fatty acids – primarily C18 (~70%) and mixed rosin acids (~30%).
Repeat dose systemic toxicity data are available for a lithium salt of C18 unsaturated fatty acids and also gum rosin. As the R groups are derived from distilled oil, the ratio of unsaturated C18 and rosin acids R groups in the molecule are likely to be proportional to the levels found in the parent distilled tall oil. The NOAEL value used as the starting point for systemic DNEL derivation is calculated proportionally, to give an estimated DNEL.
The NOAEL value is derived from a combined dermal repeat dose/reproductive toxicity screening study in rats on (Thorsrud, 2011) and an oral reproductive toxicity screening study in rats (Inveresk Research, 2003).
Based on the above calculation, a NOAEL of 849 mg/kg bw/d was derived ((70% x 1089.75 mg/kg bw/d) + (30% x 288 mg/kg bw/d)).
Dermal DNEL (systemic)
Dose descriptor
The calculated NOAEL of 849 mg/kg bw/d will be used as the starting point.
Modification of dose descriptor
100% absorption after ingestion and 100% after skin contact are assumed.
Assessment factors (ECHA Guidance Chapter R8, Table R8-6, November 2012
Long-term DNEL Assessment Factors (Dermal) |
||
Assessment Factor |
Worker |
|
Interspecies |
2.5 (for systemic effects)
4 (Allometric scaling for rats) |
|
Intraspecies |
5 (for worker) |
|
Exposure duration |
6 (subacute to chronic) |
|
Issues related to dose-response |
1 |
|
Issues related to dose-response |
1 |
|
|
||
Overall AF |
300 |
DNEL Worker long-term dermal-systemic = 849 / 300 = 2.83 mg/kg bw/day
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown but no further hazard information necessary as no exposure expected
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown but no further hazard information necessary as no exposure expected
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown but no further hazard information necessary as no exposure expected
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown but no further hazard information necessary as no exposure expected
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.415 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 600
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 849 mg/kg bw/day
- AF for dose response relationship:
- 1
- Justification:
- Default AF
- AF for differences in duration of exposure:
- 6
- Justification:
- For sub-acute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default for rat
- AF for other interspecies differences:
- 2.5
- Justification:
- Default AF
- AF for intraspecies differences:
- 10
- Justification:
- Default for general population
- AF for the quality of the whole database:
- 1
- Justification:
- default AF
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.415 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 600
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 849 mg/kg bw/day
- AF for dose response relationship:
- 1
- Justification:
- Default AF
- AF for differences in duration of exposure:
- 6
- Justification:
- Sub-acute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default for rat
- AF for other interspecies differences:
- 2.5
- Justification:
- Default AF
- AF for intraspecies differences:
- 10
- Justification:
- Default for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Default AF
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - General Population
Acute Toxicity
A DNEL for acute toxicity need only be derived if an acute hazard leading to classification for acute toxicity (under CLP [A1]) has been identified and there is a potential for high peak exposures. If no hazard has been identified then a DNEL for acute toxicity is unnecessary as the long-term DNEL will be sufficient to ensure that adverse effects do not occur. Distilled tall oil, magnesium salts are not classified for acute toxicity and are not irritant (eye, skin or respiratory tract) and therefore no acute DNELs (systemic or local) have been calculated.
Long-term Systemic Toxicity
Distilled tall oil, magnesium salts is complex reaction product formed by reacting magnesium hydroxide with distilled tall oil. It has the generic structure RCOO—Mg—OOCR, with the R groups being derived from the distilled tall oil. Distilled tall oil is a UVCB substance derived from natural sources and typical analysis shows it comprises a mixture of unsaturated fatty acids – primarily C18 (~70%) and mixed rosin acids (~30%).
Repeat dose systemic toxicity data are available for a lithium salt of C18 unsaturated fatty acids and also gum rosin. As the R groups are derived from distilled tall oil, the ratio of unsaturated C18 and rosin acids R groups in the molecule is likely to be proportional to the levels found in the parent distilled tall oil. The NOAEL value used as the starting point for systemic DNEL derivation is calculated proportionally, to give an estimated DNEL.
The NOAEL value is derived from a combined dermal repeat dose/reproductive toxicity screening study in rats (Thorsrud, 2011) and an oral reproductive toxicity screening study in rats (Inveresk Research, 2003).
Based on the above calculation, a NOAEL of 849 mg/kg bw/d was derived ((70% x 1089.75 mg/kg bw/d) + (30% x 288 mg/kg bw/d)).
Dermal DNEL (systemic)
Dose descriptor
The calculated NOAEL of 849 /kg bw/d will be used as the starting point.
Modification of dose descriptor
100% absorption after ingestion and 100% after skin contact are assumed.
Assessment factors (ECHA Guidance Chapter R8, Table R8-6, November 2012
Long-term DNEL Assessment Factors (Dermal) |
||
Assessment Factor |
General Population |
|
Interspecies |
2.5 (for systemic effects)
4 (Allometric scaling for rats) |
|
Intraspecies |
10 (for general population) |
|
Exposure duration |
6 (subacute to chronic) |
|
Issues related to dose-response |
1 |
|
Issues related to dose-response |
1 |
|
|
||
Overall AF |
600 |
DNEL General Population long-term dermal-systemic = 849 / 600 = 1.415 mg/kg bw/day
Oral DNEL (systemic)
Dose descriptor
The calculated NOAEL of 849 /kg bw/d will be used as the starting point.
Modification of dose descriptor
100% absorption after ingestion and 100% after skin contact are assumed.
Assessment factors (ECHA Guidance Chapter R8, Table R8-6, November 2012
Long-term DNEL Assessment Factors (Oral) |
||
Assessment Factor |
General Population |
|
Interspecies |
2.5 (for systemic effects)
4 (Allometric scaling for rats) |
|
Intraspecies |
10 (for general population) |
|
Exposure duration |
6 (subacute to chronic) |
|
Issues related to dose-response |
1 |
|
Issues related to dose-response |
1 |
|
|
||
Overall AF |
600 |
DNEL General Population long-term oral-systemic = 849 / 600 = 1.415 mg/kg bw/day
Read across justification for Distilled Tall Oil, Magnesium Salts
Distilled tall oil, magnesium salts is produced by reacting magnesium hydroxide and distilled tall oil. The resulting substance is a UVCB, with the following generic structure:
RCOO—Mg—OOCR
The R groups are derived from the distilled tall oil starting material, which is a UVCB substance derived from natural sources, with varying composition. Therefore there are a number of different possible combinations for the resulting carboxylic acid groups present in the complex mixture of divalent magnesium salts.
Based on supplier analysis, the distilled tall oil comprises a mixture of unsaturated fatty acids – primarily C18 (~70%) and mixed rosin acids (~30%); typical analysis of a sample of distilled tall oil is presented in Table 1. The variable composition of distilled tall oil means that Distilled tall oil, magnesium salts will comprise a complex mixture of the divalent magnesium salts of both fatty acid and rosin components, in proportion to the ratio of fatty acids:rosin acids found in the starting distilled tall oil. In the absence of data on Distilled tall oil, magnesium salts, the environmental fate, ecotoxicity and toxicology properties are predicted based on read across to related fatty acid and rosin acid salts. Analytical data (Mass Spec., FTIR and NMR) confirm the presence of divalent magnesium carboxylic acid salts and NMR shows the presence of a proportion of cyclic carboxylic acid structures.
No data were identified for magnesium salts of C18 unsaturated fatty acids, which comprises approximately 70% of the registered substance. Data were available however for a similar lithium salt – fatty acids, C18-(unsaturated) lithium salts. Read across to this compound is justified based on the fact that it is also a divalent salt of fatty acids derived from distilled tall oil, which has similar physic-chemical properties. The lithium and magnesium ions present in these salts are not likely to contribute to the toxicity and therefore any effects observed are likely to be due to the fatty acid component.
For the rosin acid salt component (~30%) of Distilled tall oil, magnesium salts, data are read across from a category of substances with similar composition, containing rosin, hydrogenated rosin and rosin acid salts. This category of rosin substances have been registered under REACH using a category approach, and members of this category are considered to be representative of the rosin acid salts found in Distilled tall oil, magnesium salts. The category of rosin substances includes both monovalent and divalent salts of rosin acids, including a magnesium salt. Therefore the rosin acid component of Distilled tall oil, magnesium salts would fit within this category and read across is considered to be appropriate.
Further details are given in the attachment in Section 13.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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