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EC number: 295-184-4 | CAS number: 91845-13-5
- 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
Adsorption / desorption
Administrative data
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Study period:
- Testing was conducted between 18 October 2010 and 17 December 2010.
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The adsorption coefficient was estimated using a computer-based atom fragment contribution method, KOCWIN, version 2.00 (February 2009), © 2000-2008 U.S. Environmental Protection Agency.
- Justification for type of information:
- No determination was possible according to Method 121 of the OECD Guidelines for Testing of Chemicals, due to the following reason: An assessment of the emulsification properties of the test item was carried out with the test item prepared in water saturated n-octanol and shaken with an equal amount of n-octanol saturated water. Observations during this test showed that the two immiscible phases emulsified easily; additionally, after 2½ hours standing, there were still three layers visible, the middle layer being a white emulsion.Surfactants are not suitable for determination by the HPLC method. Therefore, the adsorption coefficient was estimated using a computer-based atom fragment contribution method, KOCWIN, version 2.00 (February 2009), © 2000-2008 U.S. Environmental Protection Agency. Using a computer-based atom fragment contribution method, KOCWIN, version 2.00 (February 2009), © 2000-2008 U.S. Environmental Protection Agency, the adsorption coefficient (log10 Koc) of the test item was estimated to be greater than or equal to 10.0 (MCI method) and greater than or equal to 8.3 (Kow method).
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 011
- Report date:
- 2011
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- Deviations:
- no
- Principles of method if other than guideline:
- The adsorption coefficient was estimated using a computer-based atom fragment contribution method, KOCWIN, version 2.00 (February 2009), © 2000-2008 U.S. Environmental Protection Agency.
- GLP compliance:
- no
- Type of method:
- other: Estimated by calculation
- Media:
- other:
Test material
- Reference substance name:
- Additiv 309
- IUPAC Name:
- Additiv 309
- Details on test material:
- Sponsor's identification: Additiv 309
Description : Brown liquid
Batch number : 651098135
Purity : Technical:
Amine: >90% Oleylpropylenediamine(>98% Fatty acid diamine)
Water: max 0.5%
Distilled tall oil: >95% fatty acid
(ca. 5% unsaponifiables)
Date received : 03 September 2010
Expiry Date : 31 March 2012
Storage conditions: room temperature in the dark
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not Applicable - Radiolabelling:
- no
Study design
- Test temperature:
- Not Applicable
HPLC method
- Details on study design: HPLC method:
- Not Applicable
Batch equilibrium or other method
- Analytical monitoring:
- not specified
- Details on matrix:
- Not Applicable
- Details on test conditions:
- Not Applicable
- Computational methods:
- Not Applicable
Results and discussion
Adsorption coefficientopen allclose all
- Type:
- log Koc
- Value:
- >= 10
- Remarks on result:
- other: MCI method
- Type:
- log Koc
- Value:
- >= 8.3
- Remarks on result:
- other: Kow method
Results: HPLC method
- Details on results (HPLC method):
- Not Applicable
Results: Batch equilibrium or other method
- Adsorption and desorption constants:
- Not Applicable
- Recovery of test material:
- Not Applicable
- Concentration of test substance at end of adsorption equilibration period:
- Not Applicable
- Concentration of test substance at end of desorption equilibration period:
- Not Applicable
- Transformation products:
- not measured
- Details on results (Batch equilibrium method):
- Not Applicable
- Statistics:
- Not Applicable
Any other information on results incl. tables
The results are presented in the attached file "Appendix 4".
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Using a computer-based atom fragment contribution method, KOCWIN, version 2.00 (February 2009), © 2000-2008 U.S. Environmental Protection Agency, the adsorption coefficient (log10 Koc) of the test item was estimated to be greater than or equal to 10.0 (MCI method) and greater than or equal to 8.3 (Kow method).
- Executive summary:
Method
No determination was possible according to Method 121 of the OECD Guidelines for Testing of Chemicals, due to the following reason:
An assessment of the emulsification properties of the test item was carried out with the test item prepared in water saturated n-octanol and shaken with an equal amount of n-octanol saturated water. Observations during this test showed that the two immiscible phases emulsified easily; additionally, after 2½ hours standing, there were still three layers visible, the middle layer being a white emulsion.Surfactants are not suitable for determination by the HPLC method.
Therefore, the adsorption coefficient was estimated using a computer-based atom fragment contribution method, KOCWIN, version 2.00 (February 2009), © 2000-2008 U.S. Environmental Protection Agency.
Discussion
The Sponsor indicated that the test item was a complex reaction mixture of tall oil fatty acids, with (Z)-N-9-octadecenyl-1,3-propanediamine. Therefore, the limit value given in Section 10.4 was based on the initial (1:1), secondary amide reaction product of pimaric acid (the carboxylic acid group with the lowest estimated log10Pow) with the (Z)-N-9-octadecenyl-1,3-propanediamine.
Conclusion
Using a computer-based atom fragment contribution method, KOCWIN, version 2.00 (February 2009), © 2000-2008 U.S. Environmental Protection Agency, the adsorption coefficient (log10 Koc) of the test item was estimated to be greater than or equal to 10.0 (MCI method) and greater than or equal to 8.3 (Kowmethod).
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