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EC number: 688-159-8 | CAS number: 1024699-81-7
- 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
Acute Toxicity: dermal
Administrative data
- Endpoint:
- acute toxicity: dermal
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- Between 21 September 2011 and 05 October 2011
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Study conducted 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. The study report was conclusive, done to a valid guideline and the study was conducted under GLP conditions.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 011
- Report date:
- 2011
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.3 (Acute Toxicity (Dermal))
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- standard acute method
- Limit test:
- yes
Test material
- Reference substance name:
- 1024700-50-2
- Cas Number:
- 1024700-50-2
- IUPAC Name:
- 1024700-50-2
- Reference substance name:
- 3-(methacrylamidopropyl) dimethylammonium sec-C10-13-alkylbenzene sulfonate salt
- IUPAC Name:
- 3-(methacrylamidopropyl) dimethylammonium sec-C10-13-alkylbenzene sulfonate salt
- Reference substance name:
- MAPDA-ABS salt
- IUPAC Name:
- MAPDA-ABS salt
- Test material form:
- liquid: viscous
- Details on test material:
- Sponsor's identification: Benzenesulfonic acid, 4-C10-13-sec-alkyl derivs., compds. with N-[3-(dimethylamino)propyl]-2-methyl-2-propenamide (1:1)
Description : light amber coloured viscous liquid
Batch number: P1113
Purity : 96.3 w%
Date received: 01 July 2011
Expiry date : 30 March 2012
Storage conditions: room temperature in the dark
The integrity of supplied data relating to the identity, purity and stability of the test item is the responsibility of the Sponsor.
A Certificate of Analysis supplied by the Sponsor is given in Appendix 1 - (attachment 1)
Constituent 1
Constituent 2
Constituent 3
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Five male and five female Wistar (RccHan:WIST) strain rats were used.
On receipt the animals were randomly allocated to cages. The females were nulliparous and non pregnant. After an acclimatisation period of at least five days the animals were selected at random and given a number unique within the study by indelible ink-marking on the tail and a number written on a cage card. At the start of the study the animals weighed at least 200g, and were eight to twelve weeks of age. The weight variation did not exceed ±20% of the mean weight for each sex.
The animals were housed in suspended solid floor polypropylene cages furnished with woodflakes. The animals were housed individually during the 24 Hour exposure period and in groups of five, by sex, for the remainder of the study. Free access to mains drinking water and food was allowed throughout the study. The diet, drinking water and bedding were routinely analysed and were considered not to contain any contaminants that could reasonably be expected to affect the purpose or integrity of the study.
The temperature and relative humidity were set to achieve limits of 19 to 25°C and 30 to 70% respectively. Any occasional deviations from these targets were considered not to have affected the purpose or integrity of the study. The rate of air exchange was at least fifteen changes per hour and the lighting was controlled by a time switch to give twelve hours continuous light (06:00 to 18:00) and twelve hours darkness.
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.
Administration / exposure
- Type of coverage:
- semiocclusive
- Vehicle:
- unchanged (no vehicle)
- Details on dermal exposure:
- On the day before treatment the back and flanks of each animal were clipped free of hair.
Using available information on the toxicity of the test item, a group of five male and five female rats was treated with the test item at a dose level of 2000 mg/kg. - Duration of exposure:
- 24 hours
- Doses:
- 2000 mg/kg body weight
- No. of animals per sex per dose:
- 5 Male @2000 mg/kg
5 Female @2000 mg/kg - Control animals:
- not required
- Details on study design:
- On the day before treatment the back and flanks of each animal were clipped free of hair.
Using available information on the toxicity of the test item, a group of five male and five female rats was treated with the test item at a dose level of 2000 mg/kg.
The appropriate amount of test item was applied as evenly as possible to an area of shorn skin (approximately 10% (50cm2) of the total body surface area) using a graduated syringe. A piece of surgical gauze was placed over the treatment area and semi occluded with a piece of self adhesive bandage. The animals were caged individually for the 24 Hour exposure period. Shortly after dosing the dressings were examined to ensure that they were securely in place.
Due to a calculation error, two animals were given the incorrect dose (0.458g and 0.456g as opposed to the correct dose of 0.456g and 0.424g respectively). Given the discrepancy was negligible and no signs of toxicity were noted in any of the other treated animals, this deviation was considered not to affect the purpose or integrity of the study.
After the 24 Hour contact period the bandage was carefully removed and the treated skin and surrounding hair wiped with cotton wool moistened with arachis oil BP to remove any residual test item. The animals were returned to group housing for the remainder of the study period.
The animals were observed for deaths or overt signs of toxicity ½, 1, 2 and 4 hours after dosing and subsequently once daily for fourteen days.
After removal of the dressings and subsequently once daily for fourteen days, the test sites were examined for evidence of primary irritation and scored according to the following scale from Draize J H (1977) "Dermal and Eye Toxicity Tests" In: Principles and Procedures for Evaluating the Toxicity of Household Substances, National Academy of Sciences, Washington DC p.31:
EVALUATION OF SKIN REACTIONS
Erythema and Eschar Formation Value
No erythema 0
Very slight erythema (barely perceptible) 1
Well-defined erythema 2
Moderate to severe erythema 3
Severe erythema (beef redness) to slight eschar formation (injuries in depth) 4
Oedema Formation
No oedema 0
Very slight oedema (barely perceptible) 1
Slight oedema (edges of area well-defined by definite raising) 2
Moderate oedema (raised approximately 1 millimetre) 3
Severe oedema (raised more than 1 millimetre and extending beyond the area of exposure) 4
Any other skin reactions, if present were also recorded.
Individual bodyweights were recorded prior to application of the test item on Day 0 and on Days 7 and 14.
At the end of the study the animals were killed by cervical dislocation. All animals were subjected to gross necropsy. This consisted of an external examination and opening of the abdominal and thoracic cavities. The appearance of any macroscopic abnormalities was recorded. No tissues were retained. - Statistics:
- No statistical analysis was performed.
Results and discussion
Effect levels
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: 95% confidence limits not reported.
- Mortality:
- Individual mortality data are given in Table 1.
There were no deaths. - Clinical signs:
- other: Individual clinical observations are given in Table 1. There were no signs of systemic toxicity.
- Gross pathology:
- Individual necropsy findings are given in Table 5.
No abnormalities were noted at necropsy. - Other findings:
- Dermal Reactions
Individual dermal reactions are given in Table 2 and Table 3 - (attachments 2 and 3)
Signs of dermal irritation noted were very slight to well defined erythema, very slight oedema, blanching of the skin, loss of skin elasticity, haemorrhage of dermal capillaries, light brown discolouration of the epidermis, glossy skin, small superficial scattered scabs, hardened light brown coloured scab, scab lifting at edges to reveal dried blood, scab lifting to reveal glossy skin, scab undulating and scab cracking. Adverse reactions prevented accurate evaluation of erythema and oedema at the test sites of all animals.
Any other information on results incl. tables
Evaluation of Data
Data evaluations included the relationship, if any, between the exposure of the animal to the test item and the incidence and severity of all abnormalities including behavioural and clinical observations, gross lesions, bodyweight changes, mortality and any other toxicological effects.
Using the mortality data obtained, an estimate of the acute dermal median lethal dose (LD50) of the test item was made.
The results were also interpreted according to EU labelling regulations Commission Directive 2001/59/EC and Regulation (EC) No 1272/2008 for the classification, packaging and labelling of dangerous substances.
Table 1 Individual Clinical Observations and Mortality Data
Dose Level mg/kg |
Animal Number and Sex |
Effects Noted After Initiation of Exposure (Hours) |
Effects Noted After Initiation of Exposure (Days) |
||||||||||||||||
½ |
1 |
2 |
4 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
||
2000 |
1-0 Male |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1-1 Male |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-2 Male |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-3 Male |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-4 Male |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-0 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-1 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-2 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-3 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-4 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0= No signs of systemic toxicity
Table 4 Individual Bodyweights and Weekly Bodyweight Changes
Dose Level mg/kg |
Animal Number and Sex |
Bodyweight (g) at Day |
Bodyweight Change (g) During Week |
|||
0 |
7 |
14 |
1 |
2 |
||
2000 |
1-0 Male |
266 |
276 |
313 |
10 |
37 |
1-1 Male |
299 |
308 |
340 |
9 |
32 |
|
1-2 Male |
256 |
259 |
282 |
3 |
23 |
|
1-3 Male |
277 |
284 |
306 |
7 |
22 |
|
1-4 Male |
258 |
268 |
291 |
10 |
23 |
|
2-0 Female |
231 |
224 |
224 |
-7 |
0 |
|
2-1 Female |
225 |
210 |
215 |
-15 |
5 |
|
2-2 Female |
228 |
225 |
230 |
-3 |
5 |
|
2-3 Female |
212 |
215 |
207 |
3 |
-8 |
|
2-4 Female |
224 |
220 |
216 |
-4 |
-4 |
Table 5 Individual Necropsy Findings
Dose Level mg/kg |
Animal Number |
Time of Death |
Macroscopic Observations |
2000 |
1-0 Male |
Killed Day 14 |
No abnormalities detected |
1-1 Male |
Killed Day 14 |
No abnormalities detected |
|
1-2 Male |
Killed Day 14 |
No abnormalities detected |
|
1-3 Male |
Killed Day 14 |
No abnormalities detected |
|
1-4 Male |
Killed Day 14 |
No abnormalities detected |
|
2-0 Female |
Killed Day 14 |
No abnormalities detected |
|
2-1 Female |
Killed Day 14 |
No abnormalities detected |
|
2-2 Female |
Killed Day 14 |
No abnormalities detected |
|
2-3 Female |
Killed Day 14 |
No abnormalities detected |
|
2-4 Female |
Killed Day 14 |
No abnormalities detected |
Applicant's summary and conclusion
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The acute dermal median lethal dose (LD50) of the test item in the Wistar strain rat was found to be greater than 2000 mg/kg bodyweight.
The test item did not meet the criteria for classification according to EU labelling regulations Commission Directive 2001/59/EC or Regulation (EC) No 1272/2008. - Executive summary:
Introduction.
The study was performed to assess the acute dermal toxicity of the test item in the Wistar strain rat. The method was designed to be compatible with the following:
OECD Guidelines for the Testing of Chemicals No. 402 “Acute Dermal Toxicity” (adopted24 February 1987)
Method B3 Acute Toxicity (Dermal) of Commission Regulation (EC) No. 440/2008
Method.
A group of ten animals (five males and five females) was given a single, 24 hour, semi‑occluded dermal application of the undiluted test item to intact skin at a dose level of 2000 mg/kg bodyweight. Clinical signs and bodyweight development were monitored during the study. All animals were subjected to gross necropsy.
Mortality.
There were no deaths.
Clinical Observations.
There were no signs of systemic toxicity.
Dermal Irritation.
Signs of dermal irritation noted were very slight to well‑defined erythema, very slight oedema, scabbing, blanching of the skin, loss of skin elasticity, haemorrhage of dermal capillaries, light brown discolouration of the epidermis, glossy skin, scab lifting to reveal dried blood or glossy skin, scab undulating and scab cracking.
Bodyweight.
All females showed no gain in bodyweight and/or bodyweight loss during the study. All males showed expected gains in bodyweight over the study period.
Necropsy.
No abnormalities were noted at necropsy.
Conclusion.
The acute dermal median lethal dose (LD50) of the test item in the Wistar strain rat was found to be greater than 2000 mg/kg bodyweight.
The test item did not meet the criteria for classification according to EU labelling regulations Commission Directive 2001/59/EC or Regulation (EC) No 1272/2008.
Applicability of cross-reading.
This study is performed on salt of C10-13-alkylbenzene sulfonate with 3-(methacrylamidopropyl) dimethylammonium (MAPDA-ABS salt) rather than 3-(methacrylamidopropyl) trimethylammonium (MAPTA-ABS salt). Support for the read-across is separately attached to Chapter 13 of this IUCLID in the document “Justification in support of cross-reading between MAPDA-ABS salt and MAPTA-ABS salt”. The justification is build on comparable structure, the available information on toxicity of the both salt parts ABS and MAPTA resp. MAPDA, and the confirmation obtained from the available data for both substances.
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