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EC number: 701-177-3 | 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
Endpoint summary
Administrative data
Link to relevant study record(s)
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Objective of study:
- absorption
- distribution
- excretion
- Principles of method if other than guideline:
- Determination of the tendency of the test substance to adhere to the teeth and oral mucosa and the exrection and distribution of 14C from the compound swallowed and absorbed into the rat. Furthermore, the metabolism of the test material to yield radioactive CO2 was observed.
- GLP compliance:
- no
- Radiolabelling:
- yes
- Species:
- rat
- Strain:
- not specified
- Sex:
- not specified
- Route of administration:
- other: applied with a micro-pipette to teeth, oral mucosa and tongue
- Vehicle:
- water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test material was dissolved in water to form a solution having 3.36E6 counts per minute per mL of solution. - Duration and frequency of treatment / exposure:
- single treatment
- Dose / conc.:
- 2.58 other: mg/rat
- Remarks:
- Experiment A (distribution)
- Dose / conc.:
- 0.3 other: mL/rat
- Remarks:
- Experiment B (metabolism)
- No. of animals per sex per dose / concentration:
- 5 animals at 0, 4 and 24 h after application (distribution)
3 animals (metabolism) - Control animals:
- no
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: urine, faeces, blood, teeth, oral mucosa, tongue, liver, kidney and bone muscle.
- Time and frequency of sampling: at 0, 4 and 24 h after application
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine, faeces and expired CO2
- Time and frequency of sampling: 48 h
- From how many animals: 3 - Type:
- distribution
- Results:
- 1.12% teeth, 2.22% oral mucosa and 2.95% tongue; immediately after application
- Type:
- distribution
- Results:
- 0.92% teeth, 0.95% oral mucosa, 0.57% tongue, 5.44% liver and 2.78% kidney; 4 h after application
- Type:
- distribution
- Results:
- 0.79% teeth, 0.92% oral mucosa, 0.57% tongue, 1.62% liver, 0.78% kidney; 24 h after application
- Type:
- excretion
- Results:
- 0.87% faeces and 33.5% urine; 4 h after application
- Type:
- excretion
- Results:
- 1.18% faeces and 42.2% urine; 24 h after application
- Type:
- metabolism
- Results:
- 0.35% were expired as CO2; 48 h after application
- Type:
- distribution
- Results:
- 1.18% liver, 13.5% bones and 18.7% muscles; 48 h after application
- Type:
- excretion
- Results:
- 2.1% feces and 49.1% urine; 48 h after application
- Details on absorption:
- Approximately 34% of the activity of the test material was excreted in the urine over a period of 4 h after application, demonstrating rapid absorption and excretion. Some 42% of the activity was excreted during 24 h. The remainder of the activity could be accounted for approximately by estimating the total amount of activity in the blood, muscles, bone and other tissues of the body, such an estimate indicating that very little, if any, of the compound was oxidized to form CO2.
- Details on distribution in tissues:
- See Table 1 under "Any other information on results incl. tables".
- Details on excretion:
- The data demonstrated the rapid excretion of 14C from the body and suggested that little of the compound is metabolized and/or held within the tissues.
Reference
Table 1. Distribution of 14C (% of the activity administered) 48 h after application.
Organ |
Average of 3 rats (%) |
Liver |
1.18 |
Bone |
13.5 |
Muscle |
18.7 |
Feces |
2.1 |
Urine |
49.1 |
CO2 expired |
0.35 |
Description of key information
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
In accordance with Annex VIII, Column 1, Item 8.8.1 of Regulation (EC) No 1907/2006 and with Guidance on information requirements and chemical safety assessment Chapter R.7c: Endpoint specific guidance (ECHA, 2017), assessment of the toxicokinetic behaviour of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine is conducted to the extent that can be derived from the relevant available information. This comprises a qualitative assessment of the available substance specific data on physico-chemical and toxicological properties according to Guidance on information requirements and chemical safety assessment Chapter R.7c: Endpoint specific guidance (ECHA, 2017) and taking into account further available information on N-methyl-N-(C18-(unsaturated)alkanoyl)glycine.
N-methyl-N-(C18-(unsaturated)alkanoyl)glycine is a liquid. It meets the definition of a UVCB substance and its main constituent has a molecular weight of 353.54 g/mol. The water solubility and the vapour pressure of the UVCB substance have been determined to be 0.44 mg/L (21 °C; EU A.6, column elution) and 1.31E-4 Pa (20 °C; EU A.4, effusion method), respectively. The log Pow was established to be in the range ≥ 3.5 to ≤ 4.2 (20 °C; EU A.8, HPLC method), reflecting its complex composition.
Absorption
Absorption is a function of the potential of a substance to diffuse across biological membranes. The most useful parameters providing information on this potential are the molecular weight, the octanol/water partition coefficient (log Pow) value and the water solubility. The log Pow value provides information on the relative solubility of the substance in water and lipids (ECHA, 2017).
Oral
The smaller the molecule, the more easily it will be taken up. In general, molecular weights below 500 g/mol are favourable for oral absorption (ECHA, 2017). As the molecular weight of the main consitutent of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine is 353.54 g/mol, absorption of the molecules in the gastrointestinal tract is in general anticipated. Absorption after oral administration is also expected when the “Lipinski Rule of Five” (Lipinski et al., 2001; Ghose et al., 1999) is applied since all rules are fulfilled. With regard to the oral bioavailability it has been shown that after oral ingestion, the structural analogue substance Sodium lauroyl sarcosinate was not hydrolysed by either gastric or intestinal enzymes in vitro (CIR, 2001).
As no toxicokinetic data of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine are available, information obtained with the structural analogue substance Sodium N-lauroylsarcosinate are assessed. There is a study on oral absorption of Sodium N-lauroylsarcosinate which was applied at a dose of 2.6 g per animal to teeth, oral mucosa and tongue of 15 rats and at a volume of 0.3 mL per animal to a group of 3 additional rats. Five rats each were examined at the time of application, and 4 and 24 h after application; the 3 additional rats were examined 48 h after application. Immediately after administration, the mean distribution of the [14C] Sodium lauroyl sarcosinate was 1.12% in the teeth, 2.22% in the oral mucosa and 2.95% in the tongue. At 4 h, the mean distribution was 0.92% in the teeth, 0.95% in the oral mucosa, 0.57% in the tongue, 5.44% in the liver, 2.78% in the kidneys, 0.87% in the faeces and 33.5% in the urine. At 24 h the mean distribution was 0.79% in the teeth, 0.92% in the oral mucosa, 0.57% in the tongue, 1.62% in the liver, 0.78% in the kidney, 1.18% in the faeces and 42.2% in the urine. About 1% of the compound adhered to the teeth and the oral mucosa each, and 0.57% adhered to the tongue; this adherence was such that no radioactivity could be washed from those tissues by a physiological saline solution. At 48 h the mean distribution of applied radioactivity was 1.18% in the liver, 13.5% in the bones, 18.7% in the muscles, 2.1% in the faeces and 49.1% in the urine. Only 0.35% of the radioactivity was expired as CO2. The data indicated that Sodium lauroyl sarcosinate was not absorbed by the tissues of the mouth, but was swallowed and absorbed into the blood in the gastrointestinal tract at a rate of more than 80%, distributed into various tissues, not metabolised and rapidly excreted mainly in the urine (Bureau of Biological Research 1994, CIR 2001).
The available data on acute and repeated dose toxicity via the oral route of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine are also considered for assessment of oral absorption. An acute oral toxicity study conducted with N-methyl-N-(C18-(unsaturated)alkanoyl)glycine showed an LD50 value > 5000 mg/kg bw (Ciba Geigy, 1980). Clinical signs observed include dyspnoea, slight exophthalmos, slight to moderate ruffled fur and slight to moderate diarrhoea as well as a slightly curved body position. All animals recovered within 7 days. The clinical signs, however, are attributed to the irritating properties of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine rather than to a systemic toxicity. This finding is further supported by another oral acute toxicity study performed with N-methyl-N-(C18-(unsaturated)alkanoyl)glycine, resulting in an LD50 value of 9200 mg/kg bw (BASF, 1979a).
Data on repeated dose toxicity are available from a subchronic oral study with N-methyl-N-(C18-(unsaturated)alkanoyl)glycine (LPT, 2020). Only slight adverse systemic effects were observed at the highest dose. The effects observd were mostly due to the local irritant effects of the test substance and were fully reversible or demonstrated a clear trend towards complete recovery within the recovery period. A NOAEL of 300 mg/kg bw/day was derived.
Available studies show that N-methyl-N-(C18-(unsaturated)alkanoyl)glycine has a low potential for toxicity after acute and repeated exposure, but no assumptions can be made regarding the absorption potential based on the experimental data. Overall, a systemic bioavailability after oral uptake of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine is considered likely.
Dermal
It is commonly accepted that smaller molecules are taken up through the skin more easily than bigger ones; the smaller the molecule, the more easily it may be taken up. In general a molecular weight below 100 g/mol favours dermal absorption, above 500 g/mol the molecule may be too large to be absorbed (ECHA, 2017).
As the molecular weight of the main consitutent N-methyl-N-(C18-(unsaturated)alkanoyl)glycine is 353.54 g/mol, a dermal absorption of the molecules cannot be excluded.
If a substance is a skin irritant or corrosive, damage to the skin surface may enhance penetration. Furthermore, if a substance has been identified as skin sensitizer, then some uptake must have occurred previously, although it may only have been a small fraction of the applied dose (ECHA, 2017).
The available data on skin irritation/corrosion of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine are also considered for assessment of dermal absorption. Three irritation/corrosion studies are available for N-methyl-N-(C18-(unsaturated)alkanoyl)glycine. In an in vitro skin corrosion study the test item was demonstrated to be non-corrosive (Frey-Tox, 2005). In two in vivo irritation studies conducted with the neat substance, N-methyl-N-(C18-(unsaturated)alkanoyl)glycine was demonstrated to be irritating to skin (Hazleton, 1991; Ciba Geigy, 1981). Therefore, an enhanced penetration of the neat substance due to local skin damage cannot be excluded. Furthermore, no skin sensitisation potential has been identified for N-methyl-N-(C18-(unsaturated)alkanoyl)glycine.
In general, the dermal uptake of substances with a high water solubility of > 10 g/L (and log Pow < 0) will be low, as those substances may be too hydrophilic to cross the stratum corneum. Log Pow values between 1 and 4 favour dermal absorption (values between 2 and 3 are optimal), in particular if water solubility is high. In contrast, log Pow values below -1 suggest that a substance is not likely to be sufficiently lipophilic to cross the stratum corneum, therefore dermal absorption is likely to be low (ECHA, 2017). As N-methyl-N-(C18-(unsaturated)alkanoyl)glycine has a log Pow in the range ≥ 3.5 to ≤ 4.2 and a water solubility of 0.44 mg/L dermal uptake is likely to be low but cannot be excluded entirely.
Overall, N-methyl-N-(C18-(unsaturated)alkanoyl)glycine is considered to have only a low potential for dermal absorption.
Inhalation
N-methyl-N-(C18-(unsaturated)alkanoyl)glycine has a vapour pressure of 1.31E-4 Pa at 20 °C. Based on the low vapour pressure value, vapours of the substance are unlikely to be available for respiratory absorption in the lung. In humans, particles with aerodynamic diameters below 100 μm have the potential to be inhaled. Particles with aerodynamic diameters below 50 μm may reach the thoracic region and those below 15 μm the alveolar region of the respiratory tract (ECHA, 2017). Moreover, moderate log Pow values (between -1 and 4) are favourable for absorption directly across the respiratory tract epithelium by passive diffusion.
Acute inhalation toxicity studies conducted with aerosols of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine (BASF, 1979b&c) are available. The LC50 for both males and females was 1.37 mg/L air and 2.3 mg/L air, respectively. Clinical signs observed in both studies are considered to be secondary effects due to local irritation of the respiratory tract. Although not classified for respiratory irritation the substance is well-known for its effects on the respiratory tract as confirmed by its self-warning ability (instantly induces coughing) well-known from handling experience.
Overall, taking the physico-chemical parameters and the acute inhalation toxicity data into consideration, respiratory absorption of N-methyl-N-(C18-(unsaturated)alkanoyl)glycine is assumed to be possible, but expected to be rather low.
Distribution/Accumulation
The distribution of the structural analogue Sodium N-lauroylsarcosinate was investigated in the oral absorption study mentioned above where [14C]Sodium lauroyl sarcosinate was applied to teeth, oral mucosa and tongue of 15 rats at a dose of 2.6 g per animal. The distribution of the radioactivity in tissues at the time of treatment was 0.09 mg/g in the teeth, 0.1 mg/g in the oral mucosa, and 0.1 mg/g in the tongue. Four hours after treatment the distribution was 0.07 mg/g in the teeth, 0.05 mg/g in the oral mucosa, 0.02 mg/g in the tongue, 0.003 mg/g in the blood, 0.015 mg/g in the liver, 0.026 mg/g in the kidneys, 0.006 mg/g in the bones and 0.009 mg/g in the muscles. At 24 hours the distribution was 0.09 mg/g in the teeth, 0.05 mg/g in the oral mucosa, 0.02 mg/g in the tongue, 0.003 mg/g in the blood, 0.005 mg/g in the liver, 0.008 mg/g in the kidneys, 0.01 mg/g in the bones and 0.006 mg/g in the muscles (Bureau of Biological Research 1994, CIR 2001).
In other studies by the same investigators the teeth of rats were brushed with dentifrice containing 2 x 10³ µg [14C] Sodium lauroyl sarcosinate. The test substance was taken up from the dentifrice by the teeth, oral mucosa and tongue in a way that a certain amount could not be rinsed away with saline solution. However, frequent application did not cause accumulation of radioactivity in bone or muscle above the one mentioned earlier in this assessment (Bureau of Biological Research 1994, CIR 2001).
Metabolism/Excretion
In the oral absorption study described above, where [14C] Sodium N-lauroylsarcosinate was applied to teeth, oral mucosa, and tongue of 15 rats at a dose of 2.6 g per animal and at a volume of 0.3 mL per animal to a group of 3 additional rats, approximately 34% of the activity of the test material was excreted in the urine over a period of 4 h after application, demonstrating rapid absorption and excretion. Some 42% of the activity was excreted during 24 h, and approximately 49% were excreted during 48 h. The remainder of the activity could approximately be accounted for by estimating the total amount of activity in the blood, muscles, bone and other tissues of the body, indicating that very little, if any, of the compound was oxidized to form CO2 (Bureau of Biological Research 1994, CIR 2001).
In addition, further experimental data show that after oral administration of [14C] Sodium N-lauroylsarcosinate to rats 82 to 89% of a 50 mg/kg bw dose was excreted in the urine and faeces within 24 h. For the next 24 h, 1 to 2 % was excreted. Nearly all of the excreted material was found in the urine (CIR, 2001).
Finally, the fact that the major function of a group of substances structurally similar to Sarcosines and Sarcosinates, the N-acyl amino acids, would appear to be in the detoxification and excretion of xenobiotic carboxylates (Farrel, 2008) strengthens the hypothesis that the main excretion route for N-methyl-N-(C18-(unsaturated)alkanoyl)glycine is by urinary excretion.
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