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EC number: 931-534-0 | CAS number: 68439-57-6
- 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, meeting generally accepted scientific prinicples, acceptable for assessment.
Data source
Reference
- Reference Type:
- publication
- Title:
- Long-term toxicity of the surfactant alpha-olefin sulphonate (AOS) in the rat.
- Author:
- Hunter, B. and Benson, H.G.
- Year:
- 1 976
- Bibliographic source:
- Toxicology 5: 359-370
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Study was performed before actual guideline was established.
- GLP compliance:
- no
- Limit test:
- no
Test material
- Reference substance name:
- Sulfonic acids, C14-16 (even numbered)-alkane hydroxy and C14-16 (even numbered)-alkene, sodium salts
- EC Number:
- 931-534-0
- Cas Number:
- 68439-57-6
- Molecular formula:
- C(4+2n)H(9+4n)SO4Na C(4+2n)H(7+4n)SO4Na n = 5-6
- IUPAC Name:
- Sulfonic acids, C14-16 (even numbered)-alkane hydroxy and C14-16 (even numbered)-alkene, sodium salts
- Reference substance name:
- Sulfonic acids, C14-16 (even numbered)-alkane hydroxy and C14-16 (even numbered)-alkene, sodium salts
- IUPAC Name:
- Sulfonic acids, C14-16 (even numbered)-alkane hydroxy and C14-16 (even numbered)-alkene, sodium salts
- Test material form:
- other: solid
- Details on test material:
- - Name of test material (as cited in study report): alpha-olefin-sulphonate
- Analytical purity: 97.93 % active ingredient
- Impurities (identity and concentrations): moisture 1.4 %, NaOH 0.01 %, inorganic salt 0.02 %, sultones/oil 10.6 % (mainly alkane-1,4-sultone)
- Composition of test material, percentage of components: mixture of alkenyl sulphonate and hydroxyalkane sulphonate (60.4 : 39.6 % w/w); Chain-length distribution C14:C16:C18 = 25:45:30
- Other: Source: Lion Fat and Oil Co. Ltd., Tokyo, Japan; pH 7.7 (1% solution)
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- other: CFY (hysterectomy-derived from SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Anglia Laboratory Animals (formerly Carworth Europe), Huntingdon, England
- Weight at study initiation: Mean group weights males 113.5 g, females 107 g
- Housing: 5/cage
- Diet (e.g. ad libitum): Spratts Laboratory Diet No. 2 containing the test substance (except control group), ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21 ± 2
- Humidity (%): 50 ± 5
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- DIET PREPARATION
- Rate of preparation of diet (frequency): A premix of the diet containing 5000 ppm test substance was prepared each week; from this, various dietary concentrations were obtained by blending in appropriate amounts of unadulterated powdered Laboratory Diet.
- Mixing appropriate amounts with (Type of food): Spratts Laboratory Diet No. 2 - Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 104 weeks
- Frequency of treatment:
- continuously, in the diet
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
males: 39, 96, 195 mg/kg bw/day; females: 57, 132, 259 mg/kg bw/day
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
1000, 2500, 5000 ppm
Basis:
nominal in diet
- No. of animals per sex per dose:
- 50
- Control animals:
- yes, plain diet
- Details on study design:
- - Dose selection rationale: based on information from other published studies (acute, long-term, prenatal development)
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: not specified
- Cage side observations included: clinical signs
DETAILED CLINICAL OBSERVATIONS: Yes, time of onset, dimensions and locations of all palpable tumors
- Time schedule: not specifed
BODY WEIGHT: Yes
- Time schedule for examinations: initially and weekly thereafter
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
Food consumption per cage determined weekly and mean daily diet consumption was calculated.
Weekly compound intake was calculated from the consumption and group mean body weight data. The mean daily intakes over the 2 years of treatment were calculated.
FOOD EFFICIENCY:
Food conversion ratios were calculated.
WATER CONSUMPTION: Assessed by inspection of the water bottles. Regular measurement was not performed as there was no evidence of a treatment-related effect.
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: initially and after 25, 51, 78 and 104 weeks
- Dose groups that were examined: control and 5000 ppm group
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at 13, 25, 52, 78 and 103 weeks
- Anaesthetic used for blood collection: Yes (not specified)
- Animals fasted: No data
- How many animals: 10 male and 10 female animals from control and 5000 ppm groups
- Parameters examined: packed cell volume, haemoglobin, red cell count, total and differential white cell counts, mean corpuscular haemoglobin and mean cell volume
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: at 13, 25, 52, 78 and 103 weeks
- Animals fasted: No data
- How many animals: 10 male and 10 female animals from control and 5000 ppm groups
- Parameters examined: plasma urea, plasma glucose, total serum proteins (with electrophoresis and AG ratio), serum alkaline phosphatase, serum glutamic pyruvic transaminase, electrolyte levels
URINALYSIS: Yes
- Time schedule for collection of urine: at 12, 25, 51, 77 and 103 weeks
- Metabolism cages used for collection of urine: No data
- Animals fasted: No data
- Parameters examined: urine samples of 10 male and 10 female animals of the control and the 5000 ppm group wer tested for pH, specific gravity, protein, reducing substances, glucose, ketones, bile pigments, urobilin and blood pigments. In addition , the spun deposit was examined for the presence of various cell types.
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes (particular attention paid to any distortion, swelling or lesion suggestive of neoplasia; further brain, pituitary, thyroids, spleen, heart, liver, kidneys, adrenals, testes, ovaries, uterus of all animals were weighed; samples of these tissues and of lungs, cervical and mesenteric lymph nodes, thymus where present, pancreas, urinary bladder, glandular and non-glandular stomach were preserved in buffered 10% formalin; eyes were preserved in Davidson's fixative, and bone marrow smears were prepared and fixed in methanol; all nodules, tissue masses and macroscopically abnormal tissues were routinely preserved, with samples of adjacent tissue where appropriate; in addition, samples of salivary gland,trachea, oesophagus, aorta, second eye, tongue, mammary gland, jejunum, mid-colon, sciatic nerve, prostate, skeletal muscle, skin and bone were routinely preserved, but processed only if specifically required)
HISTOPATHOLOGY: Yes (adrenals, thyroids, ovaries, spleen, lymph nodes and pituitary gland performed routinely for every animal; bone marrow smears, and all macroscopically observed lesions suggestive of neoplasia were also examined; in addition, samples of important tissues from 10 male and 10 female control animals, and from 20 male and 20 female rats of the 5000 ppm group were examined for non-neoplastic changes; sections of liver and kidney from all animals examined for toxic changes were stained for fat deposits, glycogen, or basement membranes; macroscopically abnormal tissues from animals which died during the study were examined to confirm the cause of death) - Statistics:
- Differences in tumour incidence were directly compared using Fisher's Exact Probability Test as a 1-tailed test. Student's t-test was employed to assess the significance of other intergroup differences.
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- not adverse
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- CLINICAL SIGNS AND MORTALITY
No treatment-related clinical signs observed. Highest mortality occurred in the 2500 ppm group, but not significantly different from control group. No indication of a treatment-related effect. The apparent causes of death were those usually seen in this strain of rats; the more common conditions included renal and respiratory infections and tumours of the subcutaneous tissues and pituitary gland, which were distributed evenly between the groups.
BODY WEIGHT AND WEIGHT GAIN
During the first 13 weeks there were no adverse changes in growth rate. Between weeks 14 and 26, however, both males and females receiving 5000 ppm showed a slight depression of bodyweight gain.the low and mid-dose groups were not affected in this way, and between weeks 26 and 96 all treated groups achieved weight gains comparable with those of the control group.
Males of all groups showed some loss of weight during the last 2 months of the study which was probably attributable to ageing , although treated males showed greater loss than did the controls.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study)
During the first year of treatment a minor depression of food intake was recorded in female rats receiving 5000 ppm in the diet which was not apparent during the second year. Food intake of rats receiving 1000 or 2500 ppm remained comparable (within ±5%) with that of the control group throughout the study.
FOOD EFFICIENCY
Food conversion ratios were not affected by treatment.
WATER CONSUMPTION
Not examined on a regular basis as there seemed to be no treatment-related effects.
OPHTHALMOSCOPIC EXAMINATION
No treatment-related abnormalities.
HAEMATOLOGY
No significant abnormalities.
CLINICAL CHEMISTRY
No significant abnormalities.
URINALYSIS
No significant abnormalities.
ORGAN WEIGHTS
No treatment-related changes. The few statistically significant differences between controls and treated groups were considered to occur by chance or to be attributable to bodyweight differences.
GROSS PATHOLOGY
Pathological conditions seen at post mortem examination in rats sacrificed at 104 weeks were those commonly seen in old rats. Chronic respiratory disease, renal pallor and cortical scarring, pituitary enlargement, ovarian cysts and subcutaneous masses were particularly noted and were commonly seen in some rats from all groups. No treatment-related effects on the reproductive organs were observed.
HISTOPATHOLOGY: NON-NEOPLASTIC
No treatment-related changes were observed. Histopathology of macroscopically abnormal tissues from animals dying during the study did not revael any condition which could be attributed to treatment.
HISTOPATHOLOGY: NEOPLASTIC (if applicable)
There were no significant intergroup differences in the overall incidence of benign tumours, malignant tumours or tumours of any type:
Pancreatic islet cell tumours in male rats were confined to the treated groups, with the highest incidence (4 rats) occurring in the 1000 ppm group. However, the similarity to the historical controls and the absence of any dose-related trend suggests a random distribution in the present study.
Adrenal tumours were found in a total of 8 males receiving 2500 ppm. However, only 2 males were affected in the high dose group, the same amount as in the control group. Therefore, the high occurrence of adrenal tumours in the 2500 ppm males was not considerd to be treatment-related.
The highest incidence of thyroid tumours occurred among females at 2500 ppm. Again, this was not considerd to be treatment-related as the incidence of thyroid tumours in the high dose group was identical to that of the control females.
Pituitary tumours were common in both control and treated rats, with the lowest incidence among males of the high dose group.
Mammary gland tumours were very common in females of all groups, there were no significant intergroup differences. The number of females bearing multiple mammary gland tumours (2 or more) were 14/30 (47%) in the controls, 17/33 (52%) in the low-, 16/38 (42%) in the mid-, and 18/35 (51%) in the high-dose group. The apparent group mean induction periods (the average time taken for the first mammary tumour in each rat to appear) for the female groups were 84 wks for the control and low-dose groups, 83 wks for the mid- and 85 wks for the high-dose group.
HISTORICAL CONTROL DATA (if applicable)
Incidences of islet cell tumours as high as those seen in the present study have been recorded among male control CFY rats used in other studies carried out in the same laboratory.
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- >= 195 mg/kg bw/day (nominal)
- Sex:
- male
- Basis for effect level:
- other: corresponding to 5000 ppm in the diet over 2 years
- Dose descriptor:
- NOAEL
- Effect level:
- >= 259 mg/kg bw/day (nominal)
- Sex:
- female
- Basis for effect level:
- other: corresponding to 5000 ppm in the diet over 2 years
- Dose descriptor:
- NOEL
- Effect level:
- 96 mg/kg bw/day (nominal)
- Sex:
- male
- Basis for effect level:
- other: body weight gain; corresponding to 2500 ppm in the diet over 2 years
- Dose descriptor:
- NOEL
- Effect level:
- 132 mg/kg bw/day (nominal)
- Sex:
- female
- Basis for effect level:
- other: body weight gain; corresponding to 2500 ppm in the diet over 2 years
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Group mean changes in body weight:
Group |
Initial weight (g) |
Increase in body weight (g) |
|||
Wks 0-13 |
Wks 14-26 |
Wks 27-52 |
Wks 53-104 |
||
Males |
|||||
Control |
114 |
390 |
108 |
144 |
132 |
1000 ppm |
113 |
385 |
112 |
149 |
69 |
2500 ppm |
113 |
390 |
107 |
146 |
56 |
5000 ppm |
114 |
376 |
91* |
138 |
69 |
Females |
|||||
Control |
107 |
170 |
64 |
83 |
143 |
1000 ppm |
107 |
170 |
55 |
76 |
155 |
2500 ppm |
107 |
186** |
59 |
92 |
122 |
5000 ppm |
107 |
180 |
46*** |
91 |
157 |
*p<0.05
** p<0.01
***p<0.001
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.