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EC number: - | 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2015-12-16 - 2016-01-12
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2016
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- OECD Guideline for the Testing of Chemicals No. 429 "Skin Sensitization: Local Lymph Node Assay" (adopted 22 July 2010)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- Method B42 Skin Sensitization (Local Lymph Node Assay) of Commission Regulation (EC) No. 440/2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- The Department of Health of the Government of the United Kingdom
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Fatty acids, C16-18 (even numbered), reaction products with tetraethylenepentamine
- Molecular formula:
- not applicable (UVCB substance)
- IUPAC Name:
- Fatty acids, C16-18 (even numbered), reaction products with tetraethylenepentamine
- Test material form:
- solid: pellets
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA/Ca
- Remarks:
- CBA/CaOlaHsd
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Envigo RMS B.V., Inc., Horst, The Netherlands
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: 8 to 12 weeks
- Weight at study initiation: 15 to 23 g
- Housing: The animals were housed in suspended solid floor polypropylene cages furnished with softwood woodflakes. The animals were provided with environmental enrichment items which were considered not to contain any contaminant of a level that might have affected the purpose or integrity of the study.
- Diet (e.g. ad libitum): 2014C Teklad Global Rodent diet supplied by Envigo RMS (UK) Limited, Oxon, UK, ad libitum
- Water (e.g. ad libitum): mains tap water, ad libitum
- Acclimation period: at least 5 days
- Indication of any skin lesions: none stated
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 to 25 °C
- Humidity (%): 30 to 70%
- Air changes (per hr): approx 15
- Photoperiod (hrs dark / hrs light): 12 hours continuous light and 12 hours darkness
Study design: in vivo (LLNA)
- Vehicle:
- propylene glycol
- Concentration:
- 25%, 10% or 5% w/w in propylene glycol
- No. of animals per dose:
- 4
- Details on study design:
- PRE-SCREEN TESTS:
- Compound solubility: yes, propylene glycol was chosen as it produced the highest concentration that was suitable for dosing.
- Irritation: The mouse was observed twice daily on Days 1, 2 and 3 and once daily on Days 4, 5 and 6. Local skin irritation was scored daily.
- Systemic toxicity: Any clinical signs of toxicity, if present, were also recorded.
- Ear thickness measurements: The thickness of each ear was measured using a Mitutoyo 547-300S gauge (Mitutoyo Corporation), pre-dose on Day 1, post dose on Day 3 and on Day 6. Any changes in the ear thickness were noted. Mean ear thickness changes were calculated between time periods Days 1 and 3 and Days 1 and 6. A mean ear thickness increase of equal to or greater than 25% was considered to indicate excessive irritation and limited biological relevance to the endpoint of sensitization.
- Erythema scores: as set out in OECD 429
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Criteria used to consider a positive response: The test item will be regarded as a sensitizer if at least one concentration of the test item results in a threefold or greater increase in HTdR incorporation compared to control values. Any test item failing to produce a threefold or greater increase in3HTdR incorporation will be classified as a "non-sensitizer".
TREATMENT PREPARATION AND ADMINISTRATION:
Test Item Preparation and Analysis
For the purpose of the study, the test item was freshly prepared as a suspension in propylene glycol. This vehicle was chosen as it produced the highest concentration that was suitable for dosing. The test item was formulated within 2 hours of being applied to the test system. It is assumed that the formulation was stable for this duration.
No analysis was conducted to determine the homogeneity, concentration or stability of the test item formulation. This is an exception with regard to GLP and has been reflected in the GLP compliance statement.
Test Item Administration
Groups of four mice were treated with the test item at concentrations of 25%, 10% or 5% w/w in propylene glycol. The preliminary screening test suggested that the test item would not produce systemic toxicity or excessive local skin irritation at the highest suitable concentration. The mice were treated by daily application of 25 uL of the appropriate concentration of the test item to the dorsal surface of each ear for three consecutive days (Days 1> 2, 3). The test item formulation was administered using an automatic micropipette and spread over the dorsal surface of the ear using the tip of the pipette.
A further group of four mice received the vehicle alone in the same manner.
3H-Methyl Thymidine Administration
Five days following the first topical application of the test item or vehicle (Day 6) all mice were injected via the tail vein with 250 uL of phosphate buffered saline (PBS) containing 3H-methyl thymidine (3HTdR: 80 uCi/mL, specific activity 2.0 Ci/mmoL, ARC UK Ltd) giving a total of 20 \xCi to each mouse. - Positive control substance(s):
- other: Phenylacetaldehyde (>90%)
Results and discussion
- Positive control results:
- Phenylacetaldehyde, 5% v/v in proylene glycol, Stimulation Index = 9.89, Result = positive
Phenylacetaldehyde (>90%) was considered to be a sensitizer under the conditions of the test.
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Value:
- 1.21
- Test group / Remarks:
- 5% w/w of the test item in propylene glycol
- Remarks on result:
- other:
- Remarks:
- negative
- Parameter:
- SI
- Value:
- 1.17
- Test group / Remarks:
- 10% w/w of the test item in propylene glycol
- Remarks on result:
- other:
- Remarks:
- negative
- Key result
- Parameter:
- SI
- Value:
- 2.43
- Test group / Remarks:
- 25% w/w of the test item in propylene glycol
- Remarks on result:
- other:
- Remarks:
- negative
- Cellular proliferation data / Observations:
- CLINICAL OBSERVATIONS:
There were no deaths. No signs of systemic toxicity were noted in the test or control animals during the test.
BODY WEIGHTS
Body weight change of the test animals between Day 1 and Day 6 was comparable to that observed in the corresponding control group animals over the same period.
Any other information on results incl. tables
RESULTS
Preliminary Screening Test
No signs of systemic toxicity, visual local skin irritation or irritation indicated by an equal to or greater than 25% increase in mean ear thickness were noted.
Based on this information the dose levels selected for the main test were 25%, 10% and 5% w/w in propylene glycol.
Main Test
Estimation of the Proliferative Response of Lymph Node Cells
The Stimulation Index expressed as the mean radioactive incorporation for each treatment group divided by the mean radioactive incorporation of the vehicle control group are as follows:
Concentration (%w/w) in propylene glycol |
Stimulation Index |
Result |
5 |
1.21 |
Negative |
10 |
1.17 |
Negative |
25 |
2.43 |
Negative |
Clinical Observations and Mortality Data
There were no deaths. No signs of systemic toxicity were noted in the test or control animals during the test.
Body Weight
Body weight change of the test animals between Day 1 and Day 6 was comparable to that observed in the corresponding control group animals over the same period.
Tables
Clinical Observations, Body Weight and Mortality Data - Preliminary Screening Test
Concentration(%w/w) in propylene glycol |
Animal Number |
Body Weight (g) |
Day |
|||||||||
1 |
2 |
3 |
4 |
S |
6 |
|||||||
Day1 |
Day6 |
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
|||||
25 |
S-l |
19.4 |
20.2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 =No signs of systemic toxicity
Local Skin Irritation-Preliminary Screening Test
Concentration(%w/w) in propylene glycol |
Animal Number |
Local Skin Irritation |
|||||||||||
Day1 |
Day2 |
Day3 |
Day4 |
Day5 |
Day6 |
||||||||
left |
right |
left |
right |
left |
right |
left |
right |
left |
right |
left |
right |
||
25 |
S-l |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Measurement of Ear Thickness and Mean Ear Thickness Changes-Preliminary Screening Test
Concentration(%w/w) in propylene glycol |
Animal Number |
Ear Thickness Measurement (mm) |
|||||
Day1 |
Day3 |
Day6 |
|||||
pre-dose |
post dose |
||||||
left |
right |
left |
right |
left |
right |
||
25 |
S-l |
0.24 |
0.23 |
0.25 |
0.24 |
0.23 |
0.24 |
overall mean (mm) |
0.24 |
0.25 |
0.24 |
||||
overall mean ear thickness change(%) |
na |
4.26 |
0.00 |
na=Not applicable
Disintegrations per Minute, Disintegrations per Minute/Node and Stimulation Index
Concentration (% w/w) in propylene glycol |
dpm |
dpm/Nodea |
Stimulation Indexb |
Result |
Vehicle |
10259.85 |
1282.48 |
na |
na |
5 |
12409.68 |
1551.21 |
1.21 |
Negative |
10 |
11994.82 |
1499.35 |
1.17 |
Negative |
25 |
24971.41 |
3121.43 |
2.43 |
Negative |
dpm = Disintegrations per minute
a = Disintegrations per minute/node obtained by dividing the disintegrations per minute value by 8 (total number of lymph nodes)
b = Stimulation Index of 3.0 or greater indicates a positive result
na = Not applicable
Individual Clinical Observations and Mortality Data
Concentration (%w/w) in propylene glycol |
Animal Number |
Day1 |
Day2 |
Day3 |
Day4 |
Day5 |
Day6 |
|||
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
|||||
Vehicle |
1-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
5 |
2-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
10 |
3-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
25 |
4-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 =No signs of systemic toxicity
Individual Body Weights and Body Weight Change
Concentration (%w/w) in propylene glycol |
Animal Number |
Body Weight (g) |
Body Weight Change (g) |
|
Day1 |
Day6 |
|||
Vehicle |
1-1 |
19.0 |
19.9 |
0.9 |
1-2 |
20.1 |
20.5 |
0.4 |
|
1-3 |
21.8 |
22.2 |
0.4 |
|
1-4 |
21.6 |
21.4 |
-0.2 |
|
5 |
2-1 |
20.5 |
20.0 |
-0.5 |
2-2 |
18.2 |
18.9 |
0.7 |
|
2-3 |
19.0 |
19.4 |
0.4 |
|
2-4 |
21.0 |
21.3 |
0.3 |
|
10 |
3-1 |
20.0 |
20.9 |
0.9 |
3-2 |
21.8 |
21.7 |
-0.1 |
|
3-3 |
18.7 |
19.4 |
0.7 |
|
3-4 |
20.7 |
20.7 |
0.0 |
|
25 |
4-1 |
20.3 |
20.9 |
0.6 |
4-2 |
19.4 |
21.2 |
1.8 |
|
4-3 |
21.1 |
21.1 |
0.0 |
|
4-4 |
18.7 |
19.9 |
1.2 |
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Remarks:
- not sensitizing
- Conclusions:
- The study was conducted under GLP according to OECD guideline 429 on the registered substance itself. The method is to be considered scientifically reasonable with no deficiencies in documentation. Positive and negative controls gave the appropriate response. Hence, the results can be considered as reliable to assess the skin sensitization potential of Octadecanoic acid, reaction products with tetraethylenepentamine. Under the experimental conditions reported, the test item did not induce a stimulation index over 3 in the test concentrations suitable for dosing. Therefore, Octadecanoic acid, reaction products with tetraethylenepentamine is considered not to be a skin sensitiser under the test conditions of this study.
- Executive summary:
A OECD TG 429 study was performed under GLP to assess the skin sensitization potential Octadecanoic acid, reaction products with tetraethylenepentamine in the CBA/Ca strain mouse following topical application to the dorsal surface of the ear.
Following a preliminary screening test in which no clinical signs of toxicity were noted at a concentration of 25% w/w, this concentration was selected as the highest dose investigated in the main test of the Local Lymph Node Assay. Three groups, each of four animals, were treated with 50 µL (25 µL per ear) of the test item as a suspension in propylene glycol at concentrations of 25%, 10% or 5% w/w. A further group of four animals was treated with propylene glycol alone.
The Stimulation Index expressed as the mean radioactive incorporation for each treatment group divided by the mean radioactive incorporation of the vehicle control group are as follows:
Concentration (%w/w) in propylene glycol
Stimulation Index
Result
5
1.21
Negative
10
1.17
Negative
25
2.43
Negative
The test item was considered to be a non-sensitizer under the conditions of the test.
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