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EC number: 483-390-9 | CAS number: 12508-61-1
- 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 5 November - 18 November 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted to GLP in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.2600 (Skin Sensitisation)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- -
- EC Number:
- 483-390-9
- EC Name:
- -
- Cas Number:
- 12508-61-1
- Molecular formula:
- H16Mg6O17S MgSO4 • 5Mg(OH)2 • 3H2O
- IUPAC Name:
- Magnesium hydroxide sulphate trihydrate
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- other: CBA/Ca (CBA/CaOlaHsd)
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Harlan Laboratories UK Limited, Bicester, Oxon, UK
- Age at study initiation: 8 – 12 weeks
- Weight at study initiation: 15 – 23g
- Housing: The animals were individually housed in suspended solid-floor polypropylene cages furnished with softwood woodflakes
- Diet (e.g. ad libitum): Free access to food (2014 Teklad Global Rodent diet supplied by Harlan Teklad, Blackthorn, Bicester, Oxon, UK) was allowed throughout the study.
- Water (e.g. ad libitum): Free access to mains tap water was allowed throughout the study.
- Acclimation period: at least 5 days
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.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 – 25 °C
- Humidity (%): 30 – 70% relative
Any occasional deviations from these targets were considered not to have affected the purpose or integrity of the study
- Air changes (per hr): approximately 15 per hour
- Photoperiod (hrs dark / hrs light): 12 hours continuous light and 12 hours darkness
IN-LIFE DATES: 5th - 18th November 2009
Study design: in vivo (LLNA)
- Vehicle:
- acetone/olive oil (4:1 v/v)
- Concentration:
- For the purpose of the study, the test material was freshly prepared as a suspension in acetone/olive oil 4:1. This vehicle was chosen as it produced the highest concentration that was suitable for dosing. Mice were treated with the test material at concentrations of 10%, 5% or 2.5% w/w in acetone/olive oil 4:1.
- No. of animals per dose:
- Groups of five mice were treated with the test material at concentrations of 10%, 5% or 2.5% w/w in acetone/olive oil 4:1.
- Details on study design:
- PROCEDURE
PRELIMINARY SCREENING TEST
Using available information regarding the irritancy potential of the test material, a preliminary screening test was performed using one mouse. The mouse was treated by daily application of 25 µL of the test material at a concentration of 10% w/w in acetone/olive oil 4:1, to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The mouse was observed twice daily on Days 1, 2 and 3 and once daily on Days 4, 5 and 6. Any signs of toxicity or excessive local irritation noted during this period were recorded. The bodyweight was recorded on Day 1 (prior to dosing) and on Day 6.
MAIN TEST
TEST MATERIAL ADMINISTRATION
Groups of five mice were treated with the test material at concentrations of 10%, 5% or 2.5% w/w in acetone/olive oil 4:1. The preliminary screening test suggested that the test material would not produce systemic toxicity or excessive local irritation at the highest suitable concentration. The mice were treated by daily application of 25 µL of the appropriate concentration of the test material to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The test material formulation was administered usingan automatic micropipette and spread over the dorsal surface of the ear using the tip of the pipette.
A further group of five mice received the vehicle alone in the same manner.
3H-METHYL THYMIDINE ADMINISTRATION
Five days following the first topical application of the test material or vehicle (Day 6) all mice were injected via the tail vein with 250 µL of phosphate buffered saline (PBS) containing 3H-methyl thymidine (3HTdR:80µCi/mL, specific activity 2.0 Ci/mmol, ARC UK Ltd) giving a total of 20 µCi to each mouse.
OBSERVATIONS
Clinical Observations: All animals were observed twice daily on Days 1, 2 and 3 and on a daily basis on Days 4, 5 and 6. Any signs of toxicity or signs of ill health during the test were recorded.
Bodyweights: The bodyweight of each mouse was recorded on Day 1 (prior to dosing) and Day 6 (prior to termination).
TERMINAL PROCEDURES
Termination:
Five hours following the administration of 3HTdR all mice were killed by carbon dioxide asphyxiation followed by cervical separation. For each individual animal of each group the draining auricular lymph nodes were excised and processed. For each individual animal 1 mL of PBS was added to the lymph nodes.
Preparation of Single Cell Suspension:
A single cell suspension of the lymph node cells for each individual animal was prepared by gentle mechanical disaggregation through a 200-mesh stainless steel gauze. The lymph node cells were rinsed through the gauze with 4 mL of PBS into a petri dish labelled with the project number and dose concentration. The lymph node cells suspension was transferred to a centrifuge tube. The petri dish was washed with an additional 5 mL of PBS to remove all remaining lymph node cells and these were added to the centrifuge tube. The lymph node cells were pelleted at 1400 rpm (approximately 190 x gravity) for ten minutes. The pellet was resuspended in 10 mL of PBS and re-pelleted. To precipitate out the radioactive material, the pellet was resuspended in 3 mL of 5% Trichloroacetic acid (TCA).
Determination of 3HTdR Incorporation:
After approximately eighteen hours incubation at approximately 4°C, the precipitates were recovered by centrifugation at 2100 rpm (approximately 450 x gravity) for ten minutes, resuspended in 1 mL of TCA and transferred to 10 mL of scintillation fluid (Optiphase 'Trisafe'). 3HTdR incorporation was measured by β-scintillation counting. The Poly Q™ vials containing the samples and scintillation fluid were placed in the sample changer of the scintillator and left for approximately twenty minutes. The purpose of this period of time in darkness was to reduce the risk of luminescence, which has been shown to affect the reliability of the results. After approximately twenty minutes, the vials were shaken vigorously. The number of radioactive disintegrations per minute was then measured using the Beckman LS6500 scintillation system (Beckman Instruments Inc, Fullerton, CA, USA). - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- Statistical Analysis
Data was processed to give group mean values for disintegrations per minute and standard deviations where appropriate. Individual and group mean disintegrations per minute values were assessed for dose response relationships by analysis of homogeneity of variance followed by one way analysis of variance (ANOVA). In the event of a significant result from the ANOVA, pairwise comparisons were performed between control and treated groups. For homogenous datasets Dunnett's Multiple Comparison test was used and for non-homogenous datasets Dunnett's T3 Multiple Comparison Method was used.
Probability values (p) are presented as follows:
P<0.001 ***
P<0.01 **
P<0.05
P>0.05 (not significant)
Results and discussion
- Positive control results:
- CURRENT POSITIVE CONTROL STUDY FOR THE LOCAL LYMPH NODE ASSAY
Introduction.
A study was performed to assess the sensitivity of the strain of mouse used at these laboratories to a known sensitiser. The methodology for the LLNA is detailed in the OECD Guideline for the Testing of Chemicals, No. 429, and Method B.42 of Commission Regulation (EC) No. 440/2008. The study described is based on these test methods but has been refined in order to reduce the number of animals required. The reduced LLNA (rLLNA) has been endorsed by the non-Commission members of the European Centre for the Validation of Alternative Method (ECVAM) Scientific Advisory Committee (ESAC) at its 26th meeting held on 26 - 27 April 2007 at ECVAM, lspra, Italy.
Test Material: α-Hexylcinnamaldehyde, tech., 85%
Project number: 0039/1120
Study dates: 05 November 2009 to 11 November 2009
METHODS
A group of five animals was treated with 50 µl(25 µl per ear) of α-Hexylcinnamaldehyde, tech., 85% as a solution in acetone/olive oil 4:1 at a concentration of 15% v/v. A further control group of five animals was treated with acetone/olive oil 4:1 alone.
RESULTS
The Stimulation Index expressed as the mean radioactive incorporation for the treatment group divided by the mean radioactive incorporation of the vehicle control group is as follows:
Concentration (% v/v) in acetone/olive oil 4:1 Stimulation Index Result
15 3.12 Positive
CONCLUSION
α-Hexylcinnamaldehyde, tech., 85% was considered to be a sensitiser under the conditions of the test.
In vivo (LLNA)
Results
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: see Remark
- Remarks:
- Interpretation of Results The proliferation response of lymph node cells was expressed as the number of radioactive disintegrations per minute per lymph nodes from each individual animal and as the ratio of 3HTdR incorporation into lymph node cells of test nodes relative to that recorded for the control nodes (Stimulation Index). The test material will be regarded as a sensitiser if at least one concentration of the test material results in a threefold or greater increase in 3HTdR incorporation compared to control values. Any test material failing to produce a threefold or greater increase in 3HTdR incorporation will be classified as a "non-sensitiser".
Any other information on results incl. tables
RESULTS
Preliminary Screening Test
No signs of systemic toxicity were noted. Based on this information the dose levels selected for the main test were 10%, 5% and 2.5% w/w in acetone/olive oil 4:1.
Main Test
Estimation of the Proliferative Response of Lymph Node Cells
The radioactive disintegrations per minute per lymph nodes for each individual animal and the stimulation index are given in the table below.
Table 1: Individual Disintegrations per Minute and Stimulation Indices
Concentration (% w/w) in acetone/olive oil 4:1 |
Animal Number |
dpm/ Animala |
Mean dpm/Animal (Standard Deviation) |
Stimulation Indexb |
Result |
Vehicle |
1-1 |
1824.64 |
2110.33 (±224.86) |
N/A |
N/A |
1-2 |
2114.81 |
||||
1-3 |
2212.29 |
||||
1-4 |
1982.98 |
||||
1-5 |
2416.92 |
||||
2.5 |
2-1 |
2862.53 |
2705.46 (±482.20) |
1.28 |
Negative |
2-2 |
1877.63 |
||||
2-3 |
2741.92 |
||||
2-4 |
3116.39 |
||||
2-5 |
2928.81 |
||||
5 |
3-1 |
1374.34 |
2443.00 (±633.26) |
1.16 |
Negative |
3-2 |
2398.09 |
||||
3-3 |
2801.66 |
||||
3-4 |
2668.06 |
||||
3-5 |
2972.85 |
||||
10 |
4-1 |
894.33 |
1487.63 (±419.09) |
0.70 |
Negative |
4-2 |
1797.98 |
||||
4-3 |
1270.54 |
||||
4-4 |
1940.21 |
||||
4-5 |
1535.07 |
The results of the statistical analysis of the data indicated there was no significant difference between the control group and the test groups.
dpm = Disintegrations per minute
a = Total number of lymph nodes per animal is 2
b = Stimulation Index of 3.0 or greater indicates a positive result
N/A = Not applicable
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 acetone/olive oil 4:1 |
Stimulation Index |
Result |
2.5 |
1.28 |
Negative |
5 |
1.16 |
Negative |
10 |
0.70 |
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.
Bodyweight
Bodyweight changes of the test animals between Day 1 and Day 6 were comparable to those observed in the corresponding control group animals over the same period.
Applicant's summary and conclusion
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The test material was considered to be a non-sensitiser under the conditions of the test.
- Executive summary:
The study was performed to assess the skin sensitisation potential of the test material in the CBA/Ca strain mouse following topical application to the dorsal surface of the ear. The method was designed to meet the requirements of the following:
• OECD Guideline for the Testing of Chemicals No. 429 "Skin Sensitisation: Local Lymph Node Assay" (adopted 24 April 2002)
• Method B42 Skin Sensitisation (Local Lymph Node Assay) of Commission Regulation (EC) No. 440/2008
• United States Environmental Protection Agency Health Effects Test Guidelines OPPTS 870.2600 Skin Sensitisation March 2003.
The test material was considered to be a non-sensitiser under the conditions of the test.
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