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Diss Factsheets
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EC number: - | CAS number: -
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Remarks:
- the tested substance is the acid part of the compound
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 983
Materials and methods
- Objective of study:
- excretion
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- 8 male Wistar rats (160-200g) were given a single i.p. dose of 384.7 μg sodium alkylbenzene-[14C]sulfonate (DBS) (2.26±0.15 mg/kg bw) in a 0.6% physiological NaCl solution. Excretion of14C in feces and urine was monitored for 10 days.
- GLP compliance:
- not specified
Test material
Reference
- Name:
- Unnamed
- Type:
- Constituent
- Test material form:
- solid: compact
- Details on test material:
- 14C-labelled Sodium dodecylbenzene sulfonate(DBS) : It was synthesized by Attar et al. from [14C]benzene, with a specific radioactivity of 5 mCi/mmol and radiochemical purity > 98%. - Attar et al.(Synthese von Natrium- Dodecylbenzol-14C-Sulfonat, Chemosphere,4(1978), 339-343)
- Radiolabelling:
- yes
- Remarks:
- 14C-labelled Sodium alkylbenzene sulfonate
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- male Wistar rats(160-200g)
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- other: 0.6% physiological NaCl solution
- Details on exposure:
- 14C-labelled Sodium alkylbenzene sulfonate was mixed homogeneously into a powdered rat chow. The [14C]DBS-treated diet and the drinking water were given daily ad lib.
- Duration and frequency of treatment / exposure:
- 10days
Doses / concentrations
- Remarks:
- Doses / Concentrations:
single i.p. dose of 0.385mg [14C]DBS per rat(2.26 +/- 0.1 5 mg/kg bw).
- No. of animals per sex per dose / concentration:
- 8 male rats
- Control animals:
- yes
- Details on study design:
- 8 male Wistar rats (160-200 g) were kept in individual metabolism cages that allowed separate collection of urine and feces. Each rat was given a single i.p. dose of 0.3847 mg [14C]DBS in a 0.6% physiological NaCl solution. Excretion of 14C in feces and urine was monitored for 10 days.
- Details on dosing and sampling:
- 8 male rats each received a single i.p. dose of 0.3847 mg [14C]DBS per animal resulting in a dose of 2.26 +/- 0.15 mg/kg bw.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on excretion:
- Within 10 days after dosing, the animals excreted 94.5% of the dose applied, 84.7% in the first 24h.
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- Analysis of feces and urine for the acid and its metabolites :Approx. 90% of the 14C in feces and 65% in urine samples, collected from the long–term and the i.p. study, respectively, could be extracted. By means of column chromatography, a polar metabolic fraction was purified and isolated by t.l.c. techniques. Unchanged DBS could not be detected either in feces or in urine extracts. No further attempts were made to identify the polar metabolites. The metabolic studies with rhesus monkeys by Crosswell were confirmed with respect to the fact that no unchanged acid was excreted in the urine. Michael showed that 19% of LAS excreted in the feces of rats was not metabolized following a single oral dose. From the present long-term feeding and the single i.p. experiments with rats, however, it is obvious that the 14C activity in feces too, consisted only of a polar fraction.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
Single i.p. application of 0.385 mg [14C]acid/rat (2.26 +/- 0.15 mg/kg bw) resulted in a total elimanation of 94.5% within 10 days. 84.7% of the dose was elimenated in the first 24 h. All fecal and renal [14C]acid-derived activity consisted of highly polar metabolities. - Executive summary:
8 male Wistar rats (160-200g) were given a single i.p. dose of 384.7 μg sodium acid-[14C]sulfonate (DBS) (2.26±0.15 mg/kg bw) in a 0.6% physiological NaCl solution. Excretion of14C in feces and urine was monitored for 10 days.Within 10 days after dosing, the animals excreted 94.5% of the dose applied, 84.7% in the first 24h. i.p. treatment resulted in a minor14C elimination in the feces(35.0±4.6%) on the first day of the experiment, whereas renally excreted radioactivity amounted to 49.7±5.7%. From days 2-10 of the excretion study, however, the percentage of radioactive products in the feces wassignificantly higher than in the urine.The results of this experiment showed that, independent of the route of administration, the daily excretion of radioactive products occurs mainly in the feces with the exception of the first day of the i.p. experiment, when the peak of14C elimination was in the urine.
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