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Diss Factsheets
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EC number: 301-097-5 | CAS number: 93981-14-7
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- 1. HYPOTHESIS FOR THE ANALOGUE APPROACH
The following read-across hypothesis is proposed for the registered substance:
The registered substance 6-[(p-tosyl)amino]hexanoic acid, compound with 2,2',2''-nitrilotriethanol (1:1) (target substance) is manufactured directly from 6-[(p-Tosyl)amino]hexanoic acid (source substance) by simple neutralisation with triethanolamine (TEA). Other than ionization of the carboxylic acid group, the 6-[(p-Tosyl)-amino]hexanoic acid remains chemically unchanged upon salt formation. In water, the acid and amine components of the target substance dissociate completely to the source substance and TEA and these two components behave essentially as independent substances. Moreover, it is hypothesised here that TEA is non-hazardous substance and the acid component of the salt that will have a more significant impact on the outcome of any (eco)toxicological or environmental tests. Hence, the toxicity data on the source substance will accurately represent the toxicity of the target substance.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
Details are attached in Section 13 of the dataset
3. ANALOGUE APPROACH JUSTIFICATION
Details are attached in section 13 of the dataset
4. DATA MATRIX
Details are attached in section 13 of the dataset - Reason / purpose for cross-reference:
- read-across source
- Duration of test (contact time):
- d
- Reference substance:
- aniline
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Remarks:
- based on ThCO2
- Value:
- 64
- Sampling time:
- 28 d
- Remarks on result:
- other: 45 % degradation after 20 days, 10 day window criterion not fulfilled
- Details on results:
- Degradation after 28 days:
Based on CO2 Evolution: 64% - Results with reference substance:
- 60% degradation after 8 d.
- Validity criteria fulfilled:
- yes
- Remarks:
- All the test performance criteria were met and the test is valid
- Interpretation of results:
- other: when applying the 10-day-window, the test item ASCplus® is not readily biodegradable following OECD 301B and EU C.4-C respectively. As degradation reached the pass level of 60% in the course of the test, ASCplus® is considered as ultimately biodegradable
- Conclusions:
- • The test item ASCplus® (source) is considered as “not readily biodegradable“.
• The degree of biodegradation reached 64 % after 28 days.
• The 10-day-window began on day 9, at its end, 45 % degradation were reached, missing the pass level of 60 % given in the OECD guideline.
• As degradation reached the pass level of 60% in the course of the test, ASCplus® is considered as ultimately biodegradable, within 28 days.
• The abiotic degradation reached 0.7 %. - Executive summary:
The biodegradation potential of the test substance (source item) was determined in accordance with the OECD Guideline for Testing of Chemicals 301B. The test substance was tested for ready biodegradability using activated sludge of a sewage treatment plant receiving predominantly domestic sewage. The test was conducted over a period of 28 days. After 28 days the biodegradation of the test substance was recorded as 64% (based on CO2 evolution).The 10-day-window began on day 9, at its end, 45% degradation were reached, missing the pass level of 60% given in the OECD guideline. As degradation reached the pass level of 60% in the course of the test, ASCplus® is considered as ultimately biodegradable, within 28 days.
The analytical determinations indicate a degradation of the test item ASCPlus® and in parallel an increase of the metabolite 4-aminobutyric acid (ABA). The metabolite 4-N-p-Tosylglycine is produced only in minor concentration toward the end of the test. The measured test item and metabolite concentrations support the CO2 evolution data.
The test substance (source) was the carboxylic acid component of the registered substance (tosyl salt). Read-across between the tosyl salt carboxylic acid (6-[(p-Tosyl)amino]hexanoic acid) and the registered substance is considered justified as the registered substance is manufactured directly from 6-[(p-Tosyl)amino]hexanoic acid by simple neutralisation with triethanolamine (TEA). Other than ionization of the carboxylic acid group, the 6-[(p-Tosyl)amino]hexanoic acid remains chemically unchanged upon salt formation. In water, the acid and amine components of 6-[(p-Tosyl)amino]hexanoic acid, compound with 2,2’,2’’-nitrilotriethanol (1:1) dissociate completely and behave essentially as independent substances. Since TEA can be considered non-hazardous, it is the acid component of the salt that will have a more significant impact on the outcome of any (eco)toxicological or environmental tests. The pKa of the carboxylic acid group in 6-[(p-Tosyl)amino]hexanoic acid (pKa = 4.90) is the same in the free acid as it is in the TEA salt. As a result, 6-[(p-Tosyl)amino]hexanoic acid will respond to changes of pH in the same way whether it is in the salt form or as the parent carboxylic acid and hence it’s bioavailability will be the same (Further justifications for the support of read-across hypothesis are attached in Section 13).
Reference
Description of key information
After 28 days the biodegradation of the registered substance was recorded as 64% (based on CO2 evolution). The 10-day-window began on day 9, at its end, 45% degradation were reached, missing the pass level of 60 % given in the OECD guideline. As degradation reached the pass level of 60% in the course of the test, ASCplus® is considered as ultimately biodegradable, within 28 days.
Key value for chemical safety assessment
- Biodegradation in water:
- not biodegradable
- Type of water:
- freshwater
Additional information
The biodegradation potential of the test substance was determined in accordance with the OECD Guideline for Testing of Chemicals 301B. The test substance was tested for ready biodegradability using activated sludge of a sewage treatment plant receiving predominantly domestic sewage. The test was conducted over a period of 28 days. After 28 days the biodegradation of the test substance was recorded as 64% (based on CO2 evolution).The 10-day-window began on day 9, at its end, 45% degradation were reached, missing the pass level of 60% given in the OECD guideline. As degradation reached the pass level of 60% in the course of the test, ASCplus® is considered as ultimately biodegradable, within 28 days.
The analytical determinations indicate a degradation of the test item ASCPlus® and in parallel an increase of the metabolite 4-aminobutyric acid (ABA). The metabolite 4-N-p-Tosylglycine is produced only in minor concentration toward the end of the test. The measured test item and metabolite concentrations support the CO2 evolution data.
An additional study was conducted on a formulated product containing the registered substance to determine the inherent biodegradability of the formulated product. The inherent biodegradability of the test material was determined in accordance with the OECD Guideline for Testing of Chemicals 302B. The biodegradation of the substance was measured by COD analysis. 0.1825 ml/l (equivalent to 142.9 mg/l COD) of test substance was added to test vessels containing 357.1 mg/l of activated sludge. The final 56 day degradation value was determined to be 78.6% at 0.1825 ml/l of test substance. From the results of this study it can be concluded that p-TSA Triethanolamine salt does not meet the criteria for classification as 'inherently biodegradable' according to the OECD 302B method, with >70% biodegradation being achieved within the 56 day test period. The test material shows good potential for ultimate biodegradation under the conditions of this study.
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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