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EC number: 239-581-2 | CAS number: 15535-79-2
- 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

Monitoring data
Administrative data
- Endpoint:
- monitoring data
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2004-2005
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: study from National Public Health Institute, Department of Environmental Health, P.O. Box 95, FIN-70701 Kuopio, Finland, well documentated, according to standards
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 008
Materials and methods
Test guideline
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- - Population with high food consumtion
- sample of 2 ml bllod
- Analysis:
The analysis of whole blood samples (2.0 ml) was performed
according to the tissue method developed by Ikonomou et al.
(2002) with slight modifications. NaCl (1 g) used to aid in the
extraction was added in a solid form, and the derivatisation
reagent, sodium tetraethylborate, was applied as 2% solution.
Three cm of basic alumina (activated at 200 °C overnight,
90 min at 300 °C, and 200 °C until use) was loaded to a Pasteur
pipette, and the samples were eluted with 10 ml of 4% diethylether
diethylether
in hexane. On average, 27 actual whole blood samples
were analysed in each batch.
Three-level calibration was performed by spiking 2.0 ml of
whole blood with known amounts of OTCs and by treating
exactly as the true samples.Whole bloodusedfor thecalibration
samples was beforehand confirmed to be free of OTCs. - GLP compliance:
- no
- Type of measurement:
- other: concentration in human
- Media:
- other: human via environment
Test material
- Reference substance name:
- Dioctyltin compounds
- IUPAC Name:
- Dioctyltin compounds
- Test material form:
- other: in human blood
Constituent 1
Results and discussion
Concentrationopen allclose all
- Country:
- Denmark
- Location:
- Turku , blood samples form human
- Substance or metabolite:
- substance
- Conc.:
- < 0.72 other: ng/ml
- Remarks on result:
- other: L0Q = 0.72 ng/ml blood
- Country:
- Finland
- Location:
- Helsinki , blood samples form human
- Substance or metabolite:
- substance
- Conc.:
- < 0.72 other: ng/ml
- Remarks on result:
- other: L0Q = 0.72 ng/ml blood
Any other information on results incl. tables
Number of blood samples: n=300
L0Q (ng/mlblood ) = 0.72
Number of samples>LOQ = 0
133 fishermen, 94 fishermen's wives, and 73 other family members living in reasonable distance from Helsinki and Turku
Applicant's summary and conclusion
- Conclusions:
- There were no Dioctyltin compounds detected in human with high fish consumption
- Executive summary:
The objective of this study was to measure the concentrations of organotin compounds in the whole blood of Finnish male fishermen (n=133), their wives (n=94), and other family members (n=73), and to investigate their associations with background variables. The concentrations were generally low, less than the limit of quantification (LOQ) for the vast majority of compounds and samples. Of the organotin compounds (mono-, di-, and tributyltin, mono-, di-, and triphenyltin, and dioctyltin), only triphenyltin was detected in more than just a few samples (in 37 of 300 samples, LOQ=0.04 ng/ml). These were mainly the samples of fishermen (26/37) and their wives (10/37). For statistical analysis, concentrations of triphenyltin were divided into two categories, bLOQ and NLOQ. Of the different background variables, age and fish consumption contributed the most to the triphenyltin concentrations. When age and fish consumption (g/day) were divided into three categories, odds ratios comparing the highest with the lowest category were 3.88 for age (95% CI 1.36– 11.09) and 3.48 for fish consumption (1.36–8.94), respectively. Compared with females, males had an odds ratio of 1.51 of having the concentration of triphenyltin NLOQ (0.72–3.14). In no of the blood samples Dioctyltin was detected (L0Q 0.72 mg/ml) To the best of our knowledge, this study confirmed for the first time with human samples that fish consumption can be associated with triphenyltin concentration in whole blood.
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