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EC number: 226-195-4 | CAS number: 5324-84-5
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1974
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH - Refer to Section 13.2 for read-across justification document
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 974
- Report date:
- 1974
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- no
- Remarks:
- Study pre-dates GLP
- Limit test:
- no
Test material
- Reference substance name:
- Alcohol sulphate
- IUPAC Name:
- Alcohol sulphate
- Test material form:
- not specified
- Details on test material:
- Name: Alcohol sulphate
Physical state: no data
Purity test date: no data
Supplier: Lion Fat & Oil Co. Ltd., Tokyo, Japan
Constituent 1
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: East Anglian Rabbitries, Colchester, England
- Age at study initiation: Not reported
- Weight at study initiation: Not reported
- Fasting period before study: Not reported
- Housing: Individually in metal cage with wire mesh floor and maintained at 18 ± 2 ºC and 50 ± 5 % RH.
- Diet (e.g. ad libitum): Ad lib (SG-1 diet)
- Water (e.g. ad libitum): Ad lib
- Acclimation period: Not reported
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 18 ± 2 ºC
- Humidity (%): 50 ± 5 % RH
- Air changes (per hr): Not reported
- Photoperiod (hrs dark / hrs light): Not reported
IN-LIFE DATES: From: To: Not reported
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: Solutions were prepared daily as a series of graded aqueous solutions so that within each study animals in all groups were dosed orally by intragastric intubation at a standard volume. Control animals were dosed with water.
DIET PREPARATION
- Rate of preparation of diet (frequency): N/A
- Mixing appropriate amounts with (Type of food): N/A
- Storage temperature of food: N/A
VEHICLE
- Justification for use and choice of vehicle (if other than water): N/A
- Concentration in vehicle: N/A
- Amount of vehicle (if gavage): Not reported
- Lot/batch no. (if required): N/A
- Purity: N/A - Analytical verification of doses or concentrations:
- no
- Details on analytical verification of doses or concentrations:
- N/A
- Details on mating procedure:
- - Impregnation procedure: Co-housed - details not reported
- Proof of pregnancy: Observation of coitus - Duration of treatment / exposure:
- Dosing commenced on Day 6 (Day 0 = confirmation of mating) and continued up to and including Day 18
- Frequency of treatment:
- Daily
- Duration of test:
- 29 days
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0.2 mg/kg bw/day (nominal)
- Dose / conc.:
- 2 mg/kg bw/day (nominal)
- Dose / conc.:
- 300 mg/kg bw/day (nominal)
- Dose / conc.:
- 600 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- Females: 13
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: 0.2 and 2.0 mg/kg/day were chosen as likely maximum human intake estimates (from detergents). 300 and 600 mg/kg/day were investigated to provoke obvious adverse effects, the pattern of which would help in assessing the relevance of any marginal differences that might occur at the lower tested concentrations.
- Rationale for animal assignment (if not random): Not reported
- Other: N/A
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Daily
DETAILED CLINICAL OBSERVATIONS: No
BODY WEIGHT: Yes
- Time schedule: 'Regularly'
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): N/A
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): N/A
POST-MORTEM EXAMINATIONS: Yes
- Conducted on all animals either at death (during the test) or at test termination.
OTHER: N/A - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: No
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes
- Other: N/A - Fetal examinations:
- - External examinations: Yes: [all per litter]
- Soft tissue examinations: Yes: [all per litter]
- Skeletal examinations: Yes: [all per litter]
- Head examinations: No - Statistics:
- Differences in mean values were statistically analysed by non-parametric methods (Wilcoxon test) since litter values rarely, if ever, follow a normal (Gaussian) distribution; in all analyses the litter was considered as the basic sample unit.
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Toxic effects were generally associated with a principal disturbance of the gastrointestinal tract. Affected rabbits showed diarrhoea, anorexia, weight loss and cachexia prior to death (moribund animals were killed for humane reasons); total litter loss (abortion and/or total resorption) tended to occur as a secondary consequence of the primary effect on the mother.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- Mortality was only observed in the highest two concentration groups; 1/13 and 11/13 in the 300 and 600 mg/kg/day test groups, respectively.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Retarded weight gain observed in the 300 mg/kg/day test group and weight loss observed in the 600 mg/kg/day.
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- not examined
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not examined
- Details on results:
- Strong toxic effects were observed in rabbits treated at the highest test concentration including; diarrhoea, anorexia, weight loss and cachexia prior to death. 11/13 individuals died during the course of the study in the 600 mg/kg/day test group, in comparison to 2/13 and 1/13 in the control and 300 mg/kg/day test groups, respectively.
Maternal developmental toxicity
- Number of abortions:
- no effects observed
- Pre- and post-implantation loss:
- no effects observed
- Total litter losses by resorption:
- no effects observed
- Early or late resorptions:
- no effects observed
- Dead fetuses:
- no effects observed
- Changes in pregnancy duration:
- not examined
- Changes in number of pregnant:
- no effects observed
- Other effects:
- not examined
- Details on maternal toxic effects:
- At the maternally toxic dose of 600 mg/kg/day, there was an increase in foetal loss and reduced litter size, due almost entirely to total litter losses. These factors were deemed to be a secondary consequence of the maternal reaction to the test item, indicated by the fact that among the rabbits bearing young at termination litter parameters were comparable to the control group.
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 300 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- mortality
Maternal abnormalities
- Abnormalities:
- no effects observed
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- not examined
- Changes in litter size and weights:
- no effects observed
- Changes in postnatal survival:
- not examined
- External malformations:
- no effects observed
- Skeletal malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- A higher incidence of rabbit pups with extra ribs in the 300 mg/kg/day treatment group was observed. The degree of incidence was within the normal historical laboratory range so this effect was deemed to be non-significant.
- Visceral malformations:
- no effects observed
- Other effects:
- not examined
- Details on embryotoxic / teratogenic effects:
- The incidence of major, minor, visceral and skeletal abnormalities was unaffected in rabbit pups. A statisticaly significant increase in the number of pups with extra ribs was observed in the 300 mg/kg/day test group. The degree of incidence was within the normal historical laboratory range so this effect was deemed to be non-significant.
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- > 600 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- not specified
- Remarks on result:
- not determinable due to adverse toxic effects at highest dose / concentration tested
Fetal abnormalities
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Developmental effects observed:
- no
Any other information on results incl. tables
Table 2 Summary of maternal performance
Observation |
Number of animals at dosage |
||||
Control |
0.2 mg/kg/day |
2.0 mg/kg/day |
300 mg/kg/day |
600 mg/kg/day |
|
Mated |
13 |
13 |
13 |
13 |
13 |
Died |
2 |
0 |
1^ |
1 |
11 |
Non-pregnant |
1 |
1 |
2 |
1 |
0 |
Total litter loss |
0 |
1 |
0 |
2 |
0 |
With viable young |
10 |
11 |
10 |
9 |
2 |
Bodyweight change |
- |
retarded gain |
- |
retarded gain |
loss |
Table 3 Group mean litter data
Dosage (mg/kg/day) |
Number of litters ^ |
Litter size (of viable young) |
Embryonic deaths |
Implantations |
Corpora lutea |
Embryonic loss % |
Litter weight (g) |
Foetal weight (g) |
|
Pre-implantation |
Post-implantation |
||||||||
0 |
A=B=10 |
7.3 |
0.5 |
7.8 |
10.7 |
27.2 |
4.3 |
295.7 |
43.1 |
0.2 |
A=12 B=11 |
7.1 7.7 |
0.8 0.4 |
7.8 8.1 |
9.2 9.5 |
12.8 12.5 |
13.9 6.1 |
- 331.3 |
- 43.5 |
2.0 |
A=B=10 |
9.0 |
1.3 |
10.3 |
10.7 |
3.8 |
12.8 |
332.6 |
37.1 |
300 |
A=11 B=9 |
7.7 9.4 |
2.4 0.6 |
10.1 10.0 |
10.8 10.8 |
6.3 6.8 |
22.7 5.6 |
- 357.3 |
- 37.9 |
600 |
A=B=2 |
8.0 |
2.0 |
10.0 |
11.0 |
9.1 |
18.2 |
297.2 |
37.1 |
^ Mean A = includes all surviving animals showing evidence of implantation, including those with total litter loss
^ Mean B = includes only animals bearing viable young at termination
Table 4 Group mean incidence of major malformations and minor anomalies
Dose (mg/kg/day) |
Number of young |
Incidence of pups with extra lumbar ribs (mean %) ^ |
||||||||
Major malformations |
Minor anomalies^ |
|||||||||
Examined |
Affected |
Gross or visceral |
Skeletal |
|||||||
Total number |
Mean % |
Examined |
Affected |
Examined |
Affected |
|||||
Total number |
Mean % |
Total number |
Mean % |
|||||||
0 |
73 |
0 |
0 |
73 |
5 |
6.3 |
73 |
2 |
2.2 |
33.6 |
0.2 |
85 |
0 |
0 |
85 |
0 |
0 |
85 |
13 |
13.1 |
46.9 |
2.0 |
90 |
1 |
1.1 |
89 |
7 |
8.6 |
89 |
20 |
22.9 |
79.6* |
300 |
85 |
0 |
0 |
85 |
3 |
4.2 |
85 |
8 |
9.4 |
63.5 |
600 |
16 |
0 |
0 |
16 |
1 |
5.6 |
16 |
2 |
14.3 |
85.7 |
^ young showing major malformations excluded
* Wilcoxon test (p < 0.05)
Applicant's summary and conclusion
- Conclusions:
- The lowest NOAEL that could be determined for maternal toxicity was 300 mg/kg/day based on adverse clinical signs and mortality observed in the 600 mg/kg/day group.
The NOAEL for developmental toxicity could not be established due to the absence of adverse toxic effects at the highest concentration i.e. > 600 mg/kg/day.
This result is appropriate under a read-across approach for applicability to the target substance sodium octane-1-sulphonate monohydrate. - Executive summary:
Alcohol sulphate was examined for potential teratogenic and embryotoxic activity in rabbits. The test item was administered by oral gavage during days 6-18 pregnancy. Dosages employed were 0.2, 2.0, 300 and 600 mg/kg/day with each group consisting of 13 female individuals (New Zealand White).
Maternal toxicity was observed in animals treated at 600 mg/kg/day and was generally with a principle disturbance of the gastrointestinal tract, resulting in diarrhoea, anorexia, weight loss and cachexia prior to death.At the maternally toxic dose of 600 mg/kg/day, there was an increase in foetal loss and reduced litter size, due almost entirely to total litter losses. These factors were deemed to be a secondary consequence of the maternal reaction to the test item, indicated by the fact that among the rabbits bearing young at termination litter parameters were comparable to the control group
The incidence of major, minor, visceral and skeletal abnormalities was unaffected in rabbit pups. A statistically significant increase in the number of pups with extra ribs was observed in the 300 mg/kg/day test group. The degree of incidence was within the normal historical laboratory range, so this effect was deemed to be non-significant.
The lowest NOAEL that could be determined for maternal toxicity was 300 mg/kg/daybased on adverse clinical signs and mortality observed in the 600 mg/kg/day group.
The NOAEL for developmental toxicity could not be established due to the absence of adverse toxic effects at the highest concentration i.e. > 600 mg/kg/day.
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