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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: oral
Administrative data
- Endpoint:
- acute toxicity: oral
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- Between 20 September 2011 and 11 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 423 (Acute Oral toxicity - Acute Toxic Class Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.1 tris (Acute Oral Toxicity - Acute Toxic Class Method)
- Deviations:
- no
- Principles of method if other than guideline:
- The sequence of dosing may not always follow the Test Guideline as shown in the schematic diagram in attachment 1. It is Company Policy to minimisethe number of animals used on each study in accordance with UK Government Home Office guidelines.
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- acute toxic class 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 2 - (attachment 2).
Constituent 1
Constituent 2
Constituent 3
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- Female Wistar (RccHan:WIST) strain rats were used.
On receipt the animals were randomly allocated to cages. The animals 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 were eight to twelve weeks of age. The bodyweights fell within an interval of ±20% of the mean initial bodyweight of the first treated group.
The animals were housed in groups of three in suspended solid floor polypropylene cages furnished with woodflakes. With the exception of an overnight fast immediately before dosing and for approximately three to four hours after dosing, 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 would 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
- Route of administration:
- oral: gavage
- Vehicle:
- arachis oil
- Details on oral exposure:
- All animals were dosed once only by gavage, using a metal cannula attached to a graduated syringe.
- Doses:
- 2000 mg/kg
- No. of animals per sex per dose:
- 3 female @ 2000 mg/kg
3 female @ 2000 mg/kg - Control animals:
- no
- Details on study design:
- Procedure
Using available information on the toxicity of the test material, 2000 mg/kg was chosen as the starting dose.
Dose Level Concentration Dose Volume Number of Rats
(mg/kg) (mg/ml) (ml/kg) Female
2000 200 10 3
2000 200 10 3
All animals were dosed once only by gavage, using a metal cannula attached to a graduated syringe. The volume administered to each animal was calculated according to the fasted bodyweight at the time of dosing. Treatment of animals was sequential. Sufficient time was allowed between each group to confirm the survival of the previously dosed animals.
The animals were observed for deaths or overt signs of toxicity ½, 1, 2 and 4 hours after dosing and subsequently once daily for up to fourteen days.
Individual bodyweights were recorded prior to dosing and seven and fourteen days after treatment or at death.
At the end of the observation period the surviving animals were killed by cervical dislocation. All animals were subjected to gross pathological examination. This consisted of an external examination and opening of the abdominal and thoracic cavities for examination of major organs.
The appearance of any macroscopic abnormalities was recorded. No tissues were retained.
Results and discussion
- Preliminary study:
- Not applicable.
Effect levels
- Sex:
- 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.
One animal was found dead one day after dosing. - Clinical signs:
- other: Individual clinical observations are given in Table 1. Signs of systemic toxicity noted in one animal four hours after dosing were pilo-erection, hunched posture and noisy respiration. No signs of systemic toxicity were noted in surviving animals.
- Gross pathology:
- Individual necropsy findings are given in Table 3.
Abnormalities noted at necropsy of the animal that died during the study were abnormally red lungs, dark liver and dark kidneys. No abnormalities were noted at necropsy of animals that were killed at the end of the study. - Other findings:
- None
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 oral median lethal dose (LD50) of the test item was made as shown in the schematic diagram in Appendix 1 - (attachment 1).
Table 1 Individual Clinical Observations and Mortality Data
Dose Level mg/kg |
Animal Number and Sex |
Effects Noted After Dosing |
Effects Noted During Period After Dosing |
||||||||||||||||
½ |
1 |
2 |
4 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
||
2000 |
1-0 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1-1 Female |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-2 Female |
0 |
0 |
0 |
PHRn |
X |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
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 |
0= No signs of systemic toxicity
H = Hunched posture
P = Pilo-erection
Rn = Noisy respiration
X = Animal dead
Table 2 Individual Bodyweights and Weekly Bodyweight Changes
Dose Level mg/kg |
Animal Number and Sex |
Bodyweight (g) at Day |
Bodyweight (g) |
Bodyweight Gain (g) During Week |
|||
0 |
7 |
14 |
1 |
2 |
|||
2000 |
1-0 Female |
162 |
178 |
188 |
|
16 |
10 |
1-1 Female |
161 |
191 |
198 |
|
30 |
7 |
|
1-2 Female |
165 |
- |
- |
147 |
- |
- |
|
2-0 Female |
178 |
190 |
201 |
|
12 |
11 |
|
2-1 Female |
188 |
195 |
216 |
|
7 |
21 |
|
2-2 Female |
164 |
177 |
189 |
|
13 |
12 |
Table 3 Individual Necropsy Findings
Dose Level mg/kg |
Animal Number and Sex |
Time of Death |
Macroscopic Observations |
2000 |
1-0 Female |
Killed Day 14 |
No abnormalities detected |
1-1 Female |
Killed Day 14 |
No abnormalities detected |
|
1-2 Female |
Found dead Day 1 |
Lungs: abnormally red Liver: dark Kidneys: dark |
|
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 |
Applicant's summary and conclusion
- Interpretation of results:
- Category 5 based on GHS criteria
- Remarks:
- Migrated information: >2000 - 5000 mg/kg
- Conclusions:
- The acute oral median lethal dose (LD50) of the test item in the female Wistar strain rat was estimated to be greater than 2000 mg/kg bodyweight, with LD50 cut-off of 2500 mg/kg bodyweight (Globally Harmonised Classification System - Category 5 >2000 - 5000 mg/kg bodyweight).
- Executive summary:
Introduction.
The study was performed to assess the acute oral toxicity of the test item following a single oral administration in the Wistar strain rat. The method was designed to be compatible with the following:
OECD Guidelines for the Testing of Chemicals No. 423 “Acute Oral Toxicity – Acute Toxic Class Method” (adopted 17 December 2001) Method B1tris Acute Toxicity (Oral) of Commission Regulation (EC) No. 440/2008
Method.
A group of three fasted females was treated with the test item at a dose level of 2000 mg/kg bodyweight. This was followed by a further group of three fasted females at the same dose level.
The test item was administered orally as asolutioninarachis oil BP. Clinical signs and bodyweight development were monitored during the study. All animals were subjected to gross necropsy.
Mortality.
One animal was found dead one day after dosing.
Clinical Observations.
Signs of systemic toxicity noted in one animal four hours after dosing were pilo-erection, hunched posture and noisy respiration. No signs of systemic toxicity were noted in surviving animals.
Bodyweight.
The surviving animals showed expected gains in bodyweight over the study period.
Necropsy.
Abnormalities noted at necropsy of the animal that died during the study were abnormally red lungs, dark liver and dark kidneys. No abnormalities were noted at necropsy of animals that were killed at the end of the study.
Conclusion.
The acute oral median lethal dose (LD50) of the test item in the female Wistar strain rat was estimated to be greater than 2000 mg/kg bodyweight, with LD50 cut-off of 2500 mg/kg bodyweight (Globally Harmonised Classification System - Category 5 >2000 - 5000 mg/kg bodyweight).
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 and to 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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