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EC number: 931-513-6 | CAS number: 1334422-09-1
- 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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to microorganisms, other
- Remarks:
- Pseudomonas cell multiplication inhibition test
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
see "General Justification for Read-Across" attached to IUCLID section 13
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
Mutual read across from the AAPBs to one another is justified:
a) Based on the information given in section 1, it can be concluded that all AAPBs mentioned above are similar in structure, since they are manufactured from similar resp. identical precursors under similar conditions and all contain the same functional groups. Thus a common mode of action can be assumed.
b) The content of minor constituents in all products are comparable and differ to an irrelevant amount.
c) The only deviation within this group of substances is a minor variety in their fatty acid moiety, which is not expected to have a relevant impact on intrinsic toxic or ecotoxic activity and environmental fate. Potential minor impact on specific endpoints will be discussed in the specific endpoint sections.
The read-across hypothesis is based on structural similarity of target and source substances. Based on the available experimental data, including key physico-chemical properties and data from toxicokinetic, acute toxicity, irritation, sensitisation, genotoxicity and repeated dose toxicity studies, the read-across strategy is supported by a quite similar toxicological profile of all five substances.
The respective data are summarised in the data matrix; robust study summaries are included in the Technical Dossier in the respective sections.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
see "General Justification for Read-Across" attached to IUCLID section 13
3. ANALOGUE APPROACH JUSTIFICATION
see "General Justification for Read-Across" attached to IUCLID section 13
4. DATA MATRIX
see "General Justification for Read-Across" attached to IUCLID section 13 - Reason / purpose for cross-reference:
- read-across: supporting information
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 16 h
- Dose descriptor:
- EC0
- Effect conc.:
- ca. 3 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth inhibition
- Conclusions:
- The available data point on a low toxicity of C8-18 and C18 unsatd. AAPB to Pseudomonas putida (30 min/16 h EC0 = 3000 mg a.i./L nominal). The obtained results were considered to be valid for the AAPBs.
Reference
Description of key information
Data for toxicity to microorganisms are available from 4 reliable studies.
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 3 000 mg/L
Additional information
No experimental data are available for C12-18 AAPB. However, adequate and reliable results on the toxicity of C8-18 and C18 unsatd. AAPB to microorganisms are available. A justification for read-across is given below.
The toxicity of C8-18 and C18 unsatd. AAPB to Pseudomonas was investigated in four studies conducted according to national standard methods (DIN 38412, part 8 and part 27) and according to EN ISO 10712, respectively.
The toxicity of C8-18 and C18 unsatd. AAPB to Pseudomonas putida was investigated in a study conducted according to EN ISO 10712. Pseudomonas were exposed to the test material (10000 mg product/L nominal) for 16 h under static conditions. A 16 h EC0 = 3000 mg active substance/L nominal was determined.
The toxicity of C8-18 and C18 unsatd. AAPB to Pseudomonas putida was investigated in a study conducted according to DIN 38412, part 27. Pseudomonas were exposed to the test material (10000 mg product/L nominal) for 30 min under static conditions. A 30 min EC0 = 3000 mg active substance/L nominal was determined.
The toxicity of C8-18 and C18 unsatd. AAPB to Pseudomonas putida Migula was investigated in a study conducted according to DIN 38412, part 8 (Pseudomonas Zellvermehrungshemm-Test). The 16 h EC10 was found to be >10000 mg dry residue/L (nominal) which corresponds to >8450 mg a.i./L nominal assuming a content of 29.6% active matter.
The toxicity of C8-18 and C18 unsatd. AAPB to Pseudomonas putida was investigated in a study conducted according to DIN 38412, part 8 (Pseudomonas Zellvermehrungshemm-Test; Draft). The 16 h EC10 and EC50 were determined to be 15000 and 17000 mg product/L nominal, respectively. The active matter content is not reported. Assuming an active matter content of 30%, a 16 EC10 = 4500 mg a.i./L and a 16 h EC50 = 5100 mg a.i./L is obtained.
Conclusion
The available data point on a low toxicity of C8-18 and C18 unsatd. AAPB to Pseudomonas putida (30 min/16 h EC0 = 3000 mg a.i./L nominal). The obtained results were considered to be valid for the AAPBs.
Justification for read-across
For details on substance identity and detailed (eco)toxicological profiles, please refer also to the general justification for read-across attached as pdf document to IUCLID section 13.
This read-across approach is justified based on structural similarities. All AAPBs contain the same functional groups. Thus a common mode of action can be assumed.
The only deviation within this group of substances is a minor variety in their fatty acid moiety (chain length and degree of unsaturation), which is not expected to have a relevant impact on intrinsic ecotoxicological properties.
a. Structural similarity and functional groups
Alkylamidopropyl betaines (AAPBs) are – with the exception of C12 AAPB - UVCB substances (Substances of Unknown or Variable composition, Complex reaction products or Biological materials), which are defined as reaction products of natural fatty acids or oils with dimethylaminopropylamine and further reaction with sodium monochloroacetate. AAPBs are amphoteric surfactants, which are characterized by both acidic and alkaline properties.
Their general structure is:
R-C(O)-NH-(CH2)3-(N(CH3)2)+-CH2-C(O)O-
R = fatty acid moiety
The fatty acids have a mixed, slightly varying composition with an even numbered chain length from C8 to C18. Unsaturated C18 may be included. Consequently, the AAPBs differ by their carbon chain length distribution and the degree of unsaturation in the fatty acid moiety. However, Lauramidopropyl betaine (C12 fatty acid derivate) is the major ingredient of all AAPBs covered by this justification as listed in table 1 “Substance identities” of the general justification for read-across.
The substances under evaluation share structural similarities with common functional groups (quaternary amines, amide bonds and carboxymethyl groups), and fatty acid chains with differences in chain length and degree of saturation.
b. Differences
Differences in ecotoxicity of the AAPBs could potentially arise from the following facts:
-Different amounts of different carbon chain lengths (carbon chain length distribution):
Higher amounts of higher chain lengths and corresponding lower amounts of lower chain length could result in a rising average lipophilicity. However, the main component for all AAPBs is C12 AAPB. Relevant effects on ecotoxicity are not to be expected.
- Different amounts of unsaturated fatty ester moieties:
Effects may be expected for e.g. physical state, but are not considered to be of relevance for ecotoxicity.
Comparison of data on toxicity to microorganisms
Endpoints |
Source substances |
Target substance |
|
C8-18 and C18 unsatd. AAPB |
C12-18 AAPB |
Short-term toxicity to aquatic invertebrates |
key.Toxicity to microorganisms: 61789-40-0_9.1.4_Henkel_2004_EN ISO 10712
key study
EN ISO 10712 (Pseudomonas cell multiplication inhibition test), Pseudomonas putida, static, freshwater
16 h EC0 = ca. 3000 mg/L act. ingr. (nominal) based on: growth inhibition
Reliability: 2 (reliable with restrictions), no GLP |
No data, read-across |
sup.Toxicity to microorganisms: 61789-40-0_9.1.4_Henkel_2004_DIN 38412 part 27
supporting study
DIN 38412, part 27: Pseudomonas oxygen consumption inhibition test, Pseudomonas putida, static, freshwater
30 min EC0 = ca. 3000 mg/L act. ingr. (nominal) based on: respiration rate
Reliability: 2 (reliable with restrictions), no GLP |
||
sup.Toxicity to microorganisms: 61789-40-0_9.1.4_Hüls_1995_DIN 38412 L8
supporting study
DIN 38412, part 8 (Pseudomonas Zellvermehrungshemm-Test), Pseudomonas putida, static, freshwater
16 h EC10 > 8450 mg/L act. ingr. (nominal) based on: growth inhibition
Reliability: 2 (reliable with restrictions), GLP |
||
sup.Toxicity to microorganisms.61789-40-0_9.1.4_Zschimmer_Schwarz_1991_DIN 38412, part 8
Reliability: 2 (reliable with restrictions), no GLP |
The available data point on a low toxicity of C8-18 and C18 unsatd. AAPB to Pseudomonas putida (30 min/16 h EC0 = 3000 mg a.i./L nominal / 16 h EC10>8450 mg a.i./L / 16 h EC10>4500 mg a.i./L).
Quality of the experimental data of the analogues:
The available data are adequate and sufficiently reliable to justify the read-across approach.
The studies were conducted according to DIN 38412, part 8 and part 27 or EN ISO 10712, respectively and were reliable with restrictions (RL2).
The test materials used in the respective studies represent the source substance as described in the hypothesis in terms of substance identity and minor constituents.
Overall, the study results are adequate for the purpose of classification and labelling and risk assessment.
Conclusion
Based on structural similarities of the target and source substancesas presented above and in more detail in the general justification for read across, it can be concluded that the available data from the source substance C8-18 and C18 unsatd. AAPB are also valid for the target substance C12-18 AAPB.
AAPBs show a low toxicity towards microorganisms (30 min/16 h EC0 = 3000 mg a.i./L, nominal).
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