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EC number: 221-221-0 | CAS number: 3033-77-0
- 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
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption in vitro / ex vivo
- Type of information:
- other: EU Risk assessment report
- Adequacy of study:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Although the EU risk assessment report is secondary literature, all data and risk assessment for the human, health and the environment have been evaluated and reviewed by Finland prior to publication. The risk assessment report has been submitted to final approval and published in the Official Journal of the European Union C157/10 dated on 21.06.2008. Thus, it is considered the information reported are reliable with the restrictions that reliability of the data presented has not been assessed again.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- European Union Risk Assessment 2,3-epoxypropyltrimethylammonium chloride CAS RN 3033-77-0 Einecs No: 221-221-0
- Author:
- EC
- Year:
- 2 008
- Bibliographic source:
- Risk Assessment. Final approved version. Rapporteur: Finland (FIN). European communities. Printed in Italy. 147pp
Materials and methods
Test material
- Reference substance name:
- (3-chloro-2-hydroxypropyl)trimethylammonium chloride
- EC Number:
- 222-048-3
- EC Name:
- (3-chloro-2-hydroxypropyl)trimethylammonium chloride
- Cas Number:
- 3327-22-8
- Molecular formula:
- C6H15ClNO.Cl
- IUPAC Name:
- 3-chloro-2-hydroxy-N,N,N-trimethylpropan-1-aminium chloride
Constituent 1
- Radiolabelling:
- yes
Administration / exposure
- Details on study design:
- The tests were conducted using four concentrations: 0.1, 1, 20 and 65% CHPTAC in water. 14C-testosterone was used as the reference compound.
The amount of radioactivity in the receptor fluid and the residual radioactivity remaining in the skin and the stratum corneum 48-h post exposure
were determined. Samples were prepared so that the labelled and non-labelled test substances were mixed to give a concentration of 2.46 MBq of the radiolabel and the above mentioned CHPTAC percentages.
The human skin sample was obtained from a 51-year female after abdominal surgery. The sample was taken to the laboratory within one hour of dissection and directly after that the skin placed in culture. Mouse skin was taken from a 10-week-old male NMRI mouse. Subcutaneous fat was removed and part of the human skin was removed until the thickness was about 0.5 mm. The measured thicknesses were: mouse skin 0.437±0.08 mm, human skin 0.531±0.043 mm. A two-compartment model was used so that the basal membrane was in contact with the receptor fluid and the stratum
corneum was exposed to the air. A glass ring was glued to the skin membranes, which left an internal area of 0.64 cm2 for the test substance, which was applied 10 ul/cm2. The absorption was measured for 48 hours, during which the viability was monitored by the presence of lactate in the
receptor fluid. Receptor fluid samples (500 ul of total 1200 ul) were collected at 1, 2, 4, 6, 8, 20, 24, 28, 44 and 48 hours, except for the 20 % dose.
The controls were sampled for lactate at 4, 8, 20, 28 and 48 hours. After the sampling of receptor fluid, fresh fluid was added to restore the original volume. The cumulative absorption was determined by calculating the sum of sampled radioactivity. Flux constant is defined as DCTx-Ty/(x-y),
where the numerator is the increase in penetrant concentration during the linear portion of the curve and where x refers to the beginning and y to
the end of linear portion of the curve. The permeability coefficient (Kp = flux constant [ug x cm-2x h-1]/applied concentration [ug/cm-3]) was
determined using tritiated water. To determine mass balance, the remaining test substance was removed with cotton swabs and the stratum corneum was isolated by tape stripping at the end of the study. The remaining skin membrane was digested with KOH and the receptor fluid was collected.
Using scintillation counting the total radioactivity was measured in each compartment separately.
Results and discussion
Any other information on results incl. tables
In the viable human skin membranes, the amount of radioactivity in the skin after tape stripping was between 0.5 and 6.8 fold higher than the amount in the receptor fluid. In mouse skin, the amount of radioactivity was 5.3 to 17.6 times lower than the amount of radioactivity in the receptor fluid. The mean recovery of radioactivity was between 91.2 and 102.2 % in mouse and human skin membranes.
Table 7.1.2 a Results of the skin permeation study in mouse skin
Concentration of CHPTAC |
65% |
20% |
1%
|
0.1 % |
Kp-values [cm h-1] |
0.026
|
0.107 |
0.065 |
0.151 |
Flux constants μg cm-2 h-1 |
18.5 |
21 |
0.61 |
0.15 |
Relative absorption (% in receptor fluid) |
13.9
|
40.9 |
22.6 |
43.6 |
Mean total abosrption (% of the radioactivity present in the receptor fluid, the receptor compartment wash and the skin (excluding tape strips) |
13.0
|
44.9 |
29.2 |
45.0 |
Mean total abosrption (% of the radioactivity present in the receptor fluid, the receptor compartment wash and the skin (including tape strips) |
13.1 |
45.2 |
30.8 |
50.3 |
Table 7.1.2 b Results of the skin permeation study in human skin
Concentration of CHPTAC |
65% |
20% |
1%
|
0.1 % |
Kp-values [cm h-1] |
0.0005*10-3 |
0.0009*10-3 |
0.0015*10-3 |
0.0022*10-3 |
Flux constants μg cm-2 h-1 |
0.36 |
0.18 |
0.014 |
0.002 |
Relative absorption (% in receptor fluid)
|
0.053 |
0.148 |
0.534 |
0.685 |
Mean total abosrption (% of the radioactivity present in the receptor fluid, the receptor compartment wash and the skin (excluding tape strips) |
0.46 |
0.46 |
3.74 |
5.79 |
Mean total abosrption (% of the radioactivity present in the receptor fluid, the receptor compartment wash and the skin (including tape strips) |
0.8 |
1.8 |
15.2 |
14.2 |
Applicant's summary and conclusion
- Conclusions:
- Based on the findings in the in vitro skin penetration assay, a maximum penetration rate of 0.685 % was reached in the human skin.
- Executive summary:
CHPTAC’s percutaneous absorption was examined in this study, which used a 2-14C radiolabelled CHPTAC and viable human and mouse skin membranes (TNO, 2003). The results of this study can serve as a worst case estimate for EPTAC as well. Because EPTAC is slightly more polar and is likely to bind to a higher extend to the stratum corneum due to its reactive epoxide function than CHPTAC, it is therefore likely that in human skin a lower amount is dermally absorbed to lower layers of the skin and systemically available.
Based on the findings in the in vitro skin penetration assay, a maximum penetration rate of 0.685 % was reached in the human skin. Since it is recommended by the TGD that the dose retained is the skin should also be taken in consideration 5 % would then be more appropriate (0.685+ (0.685 x 6.8)). However, this factor does not take into account the amount retained in the stratum corneum. Accounting for the amount retained in the stratum corneum the average absorbed ranged between 0.1-15 %. Taking the highest percentage retained in the stratum corneum would probably be too conservative, due to factors like exfoliation, washing and other processes in which the substance is lost to outside. Moreover, the epidermal uptake is likely to occur slowly because of high water solubility (>800 g/l) and a log P of less than zero. Therefore, an absorption percentage of 6 % will be taken for the risk characterisation.
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