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EC number: 243-818-5 | CAS number: 20429-33-8
- 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
Endpoint summary
Administrative data
Link to relevant study record(s)
- Endpoint:
- basic toxicokinetics in vitro / ex vivo
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- Not reported
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Read across study
- Justification for type of information:
- Refer to Section 13 for details of the read-across justification.
- Reason / purpose for cross-reference:
- reference to other study
- Reason / purpose for cross-reference:
- read-across source
- Objective of study:
- metabolism
- Principles of method if other than guideline:
- Liver and kidney microsomes from DEHP-treated and control rats were incubated with 100 µM test substance for 30 min at 37°C in a shaking water bath. The metabolites were then separated and analysed by GC-MS.
- GLP compliance:
- no
- Radiolabelling:
- yes
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on exposure:
- Diethyl hexyl pthalate (DEHP) and control treated liver and kidney microsomes were incubated with 100 µM of test substance for 30 min at 37°C in a shaking water bath according to the method of Okita et al, 1990 .
- Duration and frequency of treatment / exposure:
- 30 min
- Dose / conc.:
- 100 other: µM
- Details on dosing and sampling:
- METABOLITE CHARACTERISATION STUDIES:
- Method of identification: Mass spectral identification (GC/MS).
- Because LDEA contains a 12-carbon side chain, LDEA hydroxylation rates were compared with the hydroxylation rates for lauric acid.
- Metabolites identified:
- yes
- Details on metabolites:
- The test substance was metabolised by rat liver microsomes to two major products that were identified by GC/MS to be the 11- hydroxyl and 12-hydroxy derivatives. The specific activities for 11- and 12-hydroxylation in microsomes prepared from control rats were 2.23±0.40 and 0.71±0.17 nmol/min/mg protein, respectively.
Treatment of rats with the cytochrome P4504A inducer and peroxisome proliferator, diethylhexyl phthalate (DEHP) increased the test substance 12-hydroxylation rate to 3.50 ± 0.48 nmol/mm/mg protein, a 5-fold increase in specific activity, whereas the 11-hydroxylase activity remained unchanged.
The specific activities of 11- and 12-hydroxylation reactions in DEHP treated rats were 1.7-fold and 3.2-fold greater than the 11- and 12-hydroxylation rates, respectively.
Incubating liver microsomes from DEHP-treated rats with a polyclonal anti-rat 4A inhibited the formation of 12-OH-test substance by 80% (3.98±0.10 vs. 0.80±0.08 nmol/min/mg protein), compared with the preimmune serum, but had no inhibitory effect on the rate of 1 1-OH-test substance formation (1.93±0.09 vs. 2.20± 0.11 nmol/min/mg protein).
Rat kidney microsomes also resulted in hydroxylation of the test substance at its 11- and 12-carbon atoms, with specific activities of 0.05±0.01 and 0.28±0.02 nmol/min/mg protein, respectively.
A 5.1-fold increase in specific activity was observed for the test substance l2-hydroxylation reaction after DEHP treatment, whereas the rate for 11-hydroxylation was similar in microsomes from control and DEHP-treated rats. - Conclusions:
- Under the study conditions, the test substance was rapidly converted into 11- and 12-hydroxy derivatives in rat liver and kidney microsomes.
- Executive summary:
A study was conducted to evaluate the in vitro metabolism of the read across substance, N,N-bis(2-hydroxyethyl)dodecanamide (C12 DEA, also known as LDEA), in liver or kidney microsomes from rat to: 1) determine the extent of its hydroxylation, 2) identify the products formed and 3) examine whether treatment with the cytochrome P4504A inducer and peroxisome proliferator diethylhexyl phthalate(DEHP) would affect hydroxylation rates. Liver and kidney microsomes from DEHP-treated and control rats were incubated with 100 µM C12 DEA for 30 min at 37°C in a shaking water bath. The metabolites were then separated and analysed by GC-MS. 97% of the hydroxylated products were identified as two major substances: 11- hydroxyl and 12-hydroxy derivatives of C12 DEA. The specific activities for C12 DEA 11- and 12-hydroxylation in microsomes prepared from control rats were 2.23±0.40 and 0.71±0.17 nmol/min/mg protein, respectively. Treatment of rats with DEHP increased the C12 DEA 12-hydroxylation specific activity 5-fold to 3.50 ± 0.48 nmol/mm/mg protein, whereas the C12 DEA 11-hydroxylase activity remained unchanged. Incubating liver microsomes from DEHP-treated rats with a polyclonal anti-rat 4A inhibited the formation of 12-OH-C12 DEA by 80% (3.98±0.10 vs. 0.80±0.08 nmol/min/mg protein), compared with the pre-immune serum, but had no inhibitory effect on the rate of 1 1-OH-C12 DEA formation (1.93±0.09 vs. 2.20± 0.11 nmol/min/mg protein). Rat kidney microsomes also resulted in hydroxylation of C12 DEA at its 11- and 12-carbon atoms, with specific activities of 0.05±0.01 and 0.28±0.02 nmol/min/mg protein, respectively. In conclusion, under the study conditions, the test substance was rapidly converted into 11- and 12-hydroxy derivatives in rat liver and kidney microsomes (Merdink, 1996).
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- Not reported
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Read across study
- Justification for type of information:
- Refer to Section 13 for details of the read across justification.
- Reason / purpose for cross-reference:
- read-across source
- Objective of study:
- toxicokinetics
- Principles of method if other than guideline:
- Three male rats were administered a single dose of (14C) test substance at 1000 mg/kg bw by oral gavage. Urine was collected 6 to 24 h post-dosing to isolate metabolites. Tissue to blood ratios (TBR) were determined by collecting adipose tissue, blood, kidney and liver 72 h post-dosing.
- GLP compliance:
- not specified
- Radiolabelling:
- yes
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Inc. (Raleigh, NC)
- Age at study initiation: 81 to 87 d
- Housing: Individual glass metabolism chambers, which allowed separate collection of carbon dioxide, urine, and feces.
- Individual metabolism cages: Yes
- Diet: Purina Rodent Chow (no. 5002), ad libitum
- Water: Ad libitum - Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- ORAL DOSE FORMULATION: 16 to 18 µCi radiolabel per dose, an appropriate amount of unlabeled LDEA and water
DOSE VOLUME: 5 mL/kg bw - Duration and frequency of treatment / exposure:
- Duration of treatment: 72 h
Frequency of treatment: Single dose - Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose / concentration:
- Three
- Control animals:
- not specified
- Details on study design:
- ANESTHESIA
- Identity: Sacrificed by overdosing with sodium pentobarbital (300 mg/kg bw) through intracardiac route - Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: Urine, faeces, blood, adipose tissue, liver and kidney
- Time and frequency of sampling: 72 h after dosing
- Method type(s) for identification: Radioactivity was determined using a Packard Tricarb 1500 Liquid Scintillation Analyzer (Packard Instrument Company, Downers Grove, IL).
- Brief description on method of analysis: Digested samples of tissues, feces, and blood in Soluene-350 (Packard Instrument Company, Meriden, CT) overnight, were bleached with perchloric acid/hydrogen peroxide before addition of scintillation cocktail (Ultima Gold).
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: Urine
- Time and frequency of sampling: 6 to 24 h after dosing
- From how many animals: samples were pooled from 3 animals
- Method type(s) for identification: Lyophilised samples of urine were analysed for metabolites using HPLC reversed- phase, further purified using cation and anion-exchange chromatography and identification of metabolites were done using mass spectrophotometry; The trimethylsilyl derivative of LDEA were prepared and analyzed by GC/MS with chemical ionisation (Thomas et.al., 1990). - Statistics:
- Values for test groups were compared by ANOVA followed by Dunnett’s test.
- Details on absorption:
- The test substance was readily absorbed
- Details on distribution in tissues:
- Tissue to blood ratio (TBR) was highest in adipose tissue and liver, which had TBRs of about 50.
- Details on excretion:
- The radiolabelled test substance was excreted mostly in urine as two polar metabolites. Approximately 60 and 80% of the dose was recovered in the urine after 24 and 72 h, respectively, and 9% of the dose was recovered in feces after 72 h.
- Metabolites identified:
- yes
- Details on metabolites:
- Urine chromatographed on a reverse phase column resulted in 2 peaks. The mass spectrum of Peak 1 was assigned as the half-acid amide of succinate and DEA (loss of 8 carbons) and Peak 2 as the adipate (loss of 6 carbons) half-acid amide.
- Conclusions:
- Under the study conditions, the substance was well absorbed and mostly excreted in urine as two polar metabolites.
- Executive summary:
A study was conducted to evaluate the absorption, distribution, metabolism and excretion of the radiolabelled read across substance, N,N-bis(2-hydroxyethyl)dodecanamide (C12 DEA, also known as LDEA) in F344 rats. Three male rats were administered a single dose of (14C) C12 DEA at 1000 mg/kg bw by oral gavage. Urine was collected 6 to 24 h post-dosing to isolate metabolites. Tissue to blood ratios (TBR) was also determined by collecting adipose tissue, blood, kidney and liver 72 h post-dosing. The results of the investigation showed that C12 DEA was well absorbed and mostly excreted in urine as two polar metabolites. Approximately 60 and 80% of the dose was recovered in urine after 24 and 72 h, respectively, and 9% of the dose was recovered in faeces after 72 h. The metabolites were isolated and characterized as the half-acid amides of succinic and of adipic acid. The TBRs were highest in the adipose and liver tissues, with values of approximately 50. Under the study conditions, the substance was well absorbed and mostly excreted in urine as two polar metabolites (Mathews, 1996).
Referenceopen allclose all
Other studies: Human liver microsome results: LDEA was also metabolised to 11- and 12-hydroxy derivatives by human liver microsomes at specific activities of 0.22±0.06 and 0.84±0.26 nmol/min/mg protein, respectively.
Other examinations: Metabolism in rat and human liver slices: LDEA partitioned well into liver slices, and about 70% of the radioactive LDEA was absorbed into the slices within 4h.The absorbed radioactivity was present mostly as parent compound. About 20 and 43% of the radioactivity present in media from the un-induced and DEHP-induced rats respectively were comprised of metabolites. About 30% of the radioactivity in the media of the human liver slice incubations was in the form of metabolites.
Analytes present in the incubation media from human and rat liver slices include the half-acid amides identified as metabolites in vivo, parent LDEA, and perhaps three other metabolites that have been identified as products of ω - and ω-1 to 4 hydroxylation (Merdink et al., 1996).
Description of key information
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
- Absorption rate - oral (%):
- 50
- Absorption rate - dermal (%):
- 10
- Absorption rate - inhalation (%):
- 100
Additional information
Oral route
In vivo testing conducted in rats with the read-across substance N,N-bis(2-hydroxyethyl)dodecanamide (C12 DEA) suggests that it is well absorbed via the oral route, then relatively rapidly metabolised to polar metabolites and excreted principally in urine (Matthews, 1996). In vitro metabolism studies with rat liver and kidney microsomes show conversion of the substance into 11- and 12-hydroxy derivatives (Merdink, 1996). Overall, based on the data, moderate to high oral absorption, relatively rapid metabolisation and low bioaccumulation of the test substance is expected. For risk assessment purposes, a default value of 50% oral absorption is therefore retained.
Dermal route
In vivo dermal absorption studies conducted with the read-across substance N,N-bis(2-hydroxyethyl)dodecanamide (C12 DEA) in rats showed that uptake was moderate; approximately 25 to 30% of the applied dose penetrated the skin in 72 h, with 3 to 5% remained associated with the dose site. Similar studies in mice indicated higher uptake: after 72 h of exposure, 50 to 70% of the applied doses were absorbed and there were no statistically significant differences in absorption across the range of doses. The difference in absorption rates between animals and human skin has been investigated and reported by The European Center for Ecotoxicology and Toxicology of Chemicals (ECETOC, 1993) as well as by the European Commission (EC, 2004). Both reports state that available in vivo and in vitro data demonstrate that all animal skin are more permeable than human skin and in particular rat skin is much more permeable than human skin by a factor 3-7. Hence, for risk assessment purposes, a value of 10% is retained.
Inhalation route
For the inhalation route, a default assumption of 100% absorption is taken for risk assessment.
References
European Center for Ecotoxicology and Toxicology of Chemicals (ECETOC) (1993). Percutaneous absorption. Monograph No. 20. http://www.ecetoc.org/wp-content/uploads/2014/08/MON-020.pdf.
European Commission (EC), DG SANCO (2004). Guidance document on dermal absorption. SANCO/222/2000 rev. 7.
https://ec.europa.eu/food/sites/food/files/plant/docs/pesticides_ppp_app-proc_guide_tox_dermal-absorp-2004.pdf.
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