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EC number: 239-594-3 | CAS number: 15546-11-9
- 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:
- sub-chronic toxicity: oral
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- Not reported
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Acceptable well-documented study report which meets basic scientific principles
Data source
Reference
- Reference Type:
- publication
- Title:
- Acute and Short-term Toxicity Studies on Di-n-butyltin Dichloride in Rats
- Author:
- Gaunt I.F., Colley J., Grasso P., Creasey M. & Gangolli S.D.
- Year:
- 1 968
- Bibliographic source:
- Fd Cosmet. Toxicol. Vol. 6, pp. 599-608. Pergamon Press 1968. Printed in Great Britain
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Deviations:
- not specified
- GLP compliance:
- no
- Remarks:
- Pre-dates GLP
- Limit test:
- no
Test material
- Reference substance name:
- Dibutyltin dichloride
- EC Number:
- 211-670-0
- EC Name:
- Dibutyltin dichloride
- Cas Number:
- 683-18-1
- IUPAC Name:
- dibutyltin dichloride
- Reference substance name:
- dibutyltin chloride
- IUPAC Name:
- dibutyltin chloride
- Details on test material:
- The sample of di-n-butyltin dichloride used in these studies was supplied by Albright & Wilson (Mfg) Ltd., London SW1. It was stated to contain 99.7 % di-n-butyltin dichloride and 0.25 % tri-n-butyltin dichloride.
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- other: CFE
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: no data
- Age at study initiation: weanling rats
- Weight at study initiation: Males: 181-189 g; Females: 147-153 g
- Fasting period before study: no data
- Housing: 4 per cage
- Diet (e.g. ad libitum): The basal diet was Spillers' Laboratory Small Animal Diet which was provided ad lib.
- Water (e.g. ad libitum): Water was provided ad lib.
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS: no data
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- not specified
- Details on oral exposure:
- no data
- Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- no data
- Duration of treatment / exposure:
- 90 day oral feed study
- Frequency of treatment:
- Daily
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
10 ppm
Basis:
nominal in diet
- Remarks:
- Doses / Concentrations:
20 ppm
Basis:
nominal in diet
- Remarks:
- Doses / Concentrations:
40 ppm
Basis:
nominal in diet
- Remarks:
- Doses / Concentrations:
80 ppm
Basis:
nominal in diet
- No. of animals per sex per dose:
- Groups of 16 male and 16 female weanling rats, housed four per cage, were fed diets containing either 0 (control), 10, 20, 40 or 80 ppm di-n-butyltin dichloride for 90 days.
- Control animals:
- yes, plain diet
- Details on study design:
- no data
- Positive control:
- none
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations: Body weight was measured weekly.
FOOD CONSUMPTION AND COMPOUND INTAKE:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
Food consumption was measured weekly.
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No data
OPHTHALMOSCOPIC EXAMINATION: No data
HAEMATOLOGY: Yes
- Time schedule for collection of blood: Haematological investigations were made at week 6 on blood from the tail veins of eight rats of each sex from the 0-, 40- and 80-ppm groups and terminally on blood from the dorsal aorta of all rats. The blood was examined for haemoglobin concentration and haematocrit value and counts were made of erythrocytes, reticulocytes and total and differential leucocytes.
URINALYSIS: Yes
- Time schedule for collection of urine: Kidney function tests were conducted at week 6 on six rats of each sex from each level of treatment and on all rats terminally. The urine was examined for colour, pH, microscopic constituents, the content of protein, glucose, bile salts, blood and tin and activity of glutamic-oxaloacetic transaminase. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
Terminally all the rats were killed and subjected to autopsy, during which a careful search was made for gross changes with special reference to the bile duct and pancreas. The brain, pituitary, heart, thyroid, liver, spleen, kidneys, adrenals and gonads were weighed. The duodenal loop with the pancreas and bile duct in situ were fixed flat so as to retain their anatomical relationship.
HISTOPATHOLOGY: Yes
Paraffin-wax sections of these organs, together with salivary gland, trachea, lungs, diaphragm, various lymph nodes, thymus, stomach, ileum, colon,caecum, rectum, urinary bladder, sternum and uterus were stained with haematoxylin and eosin for histopathological examination. - Other examinations:
- no data
- Statistics:
- no data
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- 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:
- not specified
- Details on results:
- CLINICAL SIGNS AND MORTALITY
There were no deaths at any level of feeding of di-n-butyltin dichloride (up to 80 ppm) or any effects on the behaviour or condition of the rats.
BODY WEIGHT AND WEIGHT GAIN
There was a slight reduction of growth in both sexes fed 80 ppm but this was statistically significant only in females.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study)
Some reduction in food intake was noted which may have been due to unpalatability since in the preference test, even at 10 ppm, there was a marked preference for the basal diet.
HAEMATOLOGY
In the haematological examination there were decreases in haemoglobin concentrations. These were confined to the highest level of feeding (80 ppm) and seen in females at week 6 and males at week 13. The decreases, although statistically significant were slight and not associated with reductions of other erythrocyte parameters or with a reticulocytosis.
URINALYSIS
There were no deviations from normal in the serum-urea or -enzyme levels or in the urine parameters measured. Tin was not found in any of the urine samples examined.
NEUROBEHAVIOUR
No effects on the behaviour were seen.
ORGAN WEIGHTS
There were, no changes in relative organ weights.
GROSS PATHOLOGY
No abnormalities were seen at autopsy.
HISTOPATHOLOGY: NON-NEOPLASTIC
There were no differences between test and control animals in the findings in any of the tissues examined.
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 40 ppm
- Sex:
- male/female
- Basis for effect level:
- other: This dietary concentration is equivalent to an intake of 2 mg/kg/day based on measured feed intake
- Dose descriptor:
- LOAEL
- Effect level:
- 80 ppm
- Sex:
- male/female
- Basis for effect level:
- other: There was a slight reduction of growth and food intake (possibly due to unpalability) at this dietary level. The only other finding was a mild anaemia.
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
There was a slight reduction of growth and food intake at the highest dietary level. The only other finding was a mild anaemia at the 80 ppm level.
This study has shown that the no-effect level of di-n-butyltin dichloride in the diet of rats for 90 days is 40 ppm, with only very marginal changes at twice this level. This dietary concentration is equivalent to an intake of 2 mg/kg/day.
Applicant's summary and conclusion
- Conclusions:
- This study has shown that the no-effect level of di-n-butyltin dichloride in the diet of rats for 90 days is 40 ppm (40 mg/kg bw/day), with only very marginal changes at twice this level. This dietary concentration is equivalent to an intake of 2 mg/kg/day.
- Executive summary:
In a 90 day feeding study in male and female rats the no-effect level of di-n-butyltin dichloride is 40 ppm (40 mg/kg bw/day), with only very marginal changes at twice this level. This dietary concentration is equivalent to an intake of 2 mg/kg/day.
There were no deaths at any level of feeding of di-n-butyltin dichloride (up to 80 ppm (80 mg/kg bw/day)) or any effects on the behaviour or condition of the rats. There was a slight reduction of growth in both sexes fed 80 ppm (80 mg/kg bw/day) but this was statistically significant only in females. It was accompanied by some reduction in food intake which may have been due to unpalatability since in the preference test, even at 10 ppm (10 mg/kg bw/day), there was a marked preference for the basal diet. In the haematological examination there were decreases in haemoglobin concentrations. These were confined to the highest level of feeding (80 ppm (80 mg/kg bw/day)) and seen in females at week 6 and males at week 13. The decreases, although statistically significant were slight and not associated with reductions of other erythrocyte parameters or with a reticulocytosis. There were no deviations from normal in the serum-urea or -enzyme levels or in the urine parameters measured. Tin was not found in any of the urine samples examined. There were, no changes in relative organ weights and no abnormalities were seen at autopsy. There were no differences between test and control animals in the findings in any of the tissues examined.
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