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EC number: 204-340-2 | CAS number: 119-64-2
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1994-04-07 to 1994-05-19
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other:
- Remarks:
- Comparable to guideline study
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
- Report date:
- 1995
- Reference Type:
- publication
- Title:
- Modeling of residual variability in toxicokinetic studies with sparse sampling: the case of tetrahydronaphthalene
- Author:
- Meineke I, Eisele J, Certa H and Gundert-Remy UM
- Year:
- 1 998
- Bibliographic source:
- Arch. Toxicol. 72, 807-810
Materials and methods
- Objective of study:
- toxicokinetics
- Principles of method if other than guideline:
- Directive 84/449/EEC, B.7 (1992), modified
- GLP compliance:
- yes
Test material
- Reference substance name:
- 1,2,3,4-tetrahydronaphthalene
- EC Number:
- 204-340-2
- EC Name:
- 1,2,3,4-tetrahydronaphthalene
- Cas Number:
- 119-64-2
- Molecular formula:
- C10H12
- IUPAC Name:
- 1,2,3,4-tetrahydronaphthalene
- Details on test material:
- tetrahydronaphthalene of Hüls AG, produced 02 February 1993
Purity 98.5 %
Sample No. 0099 (internal)
Sample ID 3633/81495
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ORGANISMS
- Strain: Wistar (Hsd/Win:WU)
- Source: Harlan Winkelmann, Borchen (Germany)
- Age: 6 - 8 weeks
- Weight at study initiation:
range of group mean weights, males: 190-200 g
range of group mean weights, females: 146-155 g
- Number of animals: total 30 males, 30 females
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- ADMINISTRATION / EXPOSURE
- Vehicle: corn oil
- Total volume applied: 2 ml/kg bw - Duration and frequency of treatment / exposure:
- 28 day(s)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Males: vehicle; 15; 50; 150 mg/kg bw d; 150 mg/kg bw d reversal group
Females: vehicle; 15; 50; 150 mg/kg bw d; 150 mg/kg bw d reversal group
- No. of animals per sex per dose / concentration:
- Males: 5 Females: 5
- Control animals:
- yes, concurrent vehicle
- Positive control reference chemical:
- no
- Details on study design:
- SATELLITE GROUPS AND REASONS THEY WERE ADDED: additional 150 mg/kg bw d and control group for recovery study
- Details on dosing and sampling:
- CLINICAL OBSERVATIONS AND FREQUENCY:
- Clinical signs: twice daily (weekends: once daily); detailed once a week
- Mortality: twice daily (weekends: once daily)
- Body weight: before first treatment, weekly thereafter until day of necropsy
- Food consumption: weekly for each cage (5 rats/cage)
- Water consumption: daily for each cage
- Ophthalmoscopic examination: control and high dose groups during acclimatization and prior to terminal bleeding
- Haematology: all animals once (terminal) for serum chemical and haematological investigations plus twice for toxicokinetics during study
(high dose group days 1 and 16; medium and low dose groups days 3 and 18 of treatment); detailed sampling times (approximately): sampling 0.5; 1.5; 3.0; 6.0; 23.0 hours after treatment on days 1 and 16 from one animal per sex and group each; sampling on days 2 and 17 from control
groups sampling 0.5; 1.5; 6.0 hours after treatment on days 3 and 18 from 2; 2; 1 animals per sex and group additional sampling from two animals each of the high dose groups at five different times during the 14 day reversal period (first sampling was from non-reversal animals before their
sacrifice); 200-500 ul/sample
- Urinalysis: end of study; non-satellite groups additionally on days 3 (males) and 4 (females)
ORGANS EXAMINED AT NECROPSY (MACROSCOPIC AND MICROSCOPIC):
- Macroscopic: weights of adrenals, kidneys, liver, spleen, testes adrenals, aorta (thoracic), anus, brain, caecum, coagulation gland, colon,
concha (tattooed), duodenum, epididymides, eyes, exorbital lacrimal glands, gross lesions, heart, ileum, jaw (upper), jejunum, kidneys, larynx,
liver, lungs, lymph nodes (skin, cervical & mesenteric), mammary gland, muscle (skeletal), ovaries, oesophagus, pancreas, pituitary, prostate,
rectum, salivary glands, sciatic nerve, seminal vesicles, skin, spinal cord (cervical), spleen, stomach, testes, thymus, thyroid / parathyroid, tongue,
trachea, urinary bladder, uterus, vagina bone marrow smears -
- Microscopic: eyes, kidney, liver, lung, lymph nodes, oesophagus, Peyer's patches, spleen, uterus
OTHER EXAMINATIONS: toxicokinetics: see separate report and entry DEVIATIONS FROM PROTOCOL: No fixation of tibia during necropsy - Statistics:
- STATISTICAL METHODS:
- Kruskal Wallis non parametric analysis of variance, in case of significance followed by Wilcoxon, Mann, and Whitney U tests: body weights, body
weight changes, organ weights, differential blood count, urine analysis data - one way analysis of variance (ANOVA) incorporating Bartlett's test
for homogeneity of variance and if indicated followed by Kruskal Wallis or Scheffe Test: haematological data (except differential blood count) and
serum clinical chemistry data
- Median (geometric mean), minimum, maximum: differential blood count
Results and discussion
Toxicokinetic / pharmacokinetic studies
Toxicokinetic parametersopen allclose all
- Toxicokinetic parameters:
- half-life 1st: 1.5 hours
- Toxicokinetic parameters:
- half-life 2nd: 4.7 hours
- Toxicokinetic parameters:
- half-life 3rd:
Metabolite characterisation studies
- Metabolites identified:
- not measured
Any other information on results incl. tables
|
|
Maximum concentration |
Area under the curve (AUC) (µg*h/mL) |
||
Sex |
First day |
Second day |
First sampling |
Second sampling |
|
Low dose 15 mg/kg bw |
male |
0.78 mg/L (36 min) |
0.62 mg/l (34 min) |
1.70 |
1.57 |
female |
0.76 mg/L (30 min) |
1.35 mg/l (29 min) |
1.22 |
2.61 |
|
Mid dose 50 mg/kg bw |
male |
2.57 mg/L (99 min) |
1.04 mg/l (90 min) |
6.81 |
6.29 |
female |
3.46 mg/L (43 min) |
3.14 mg/l (84 min) |
5.91 |
8.26 |
|
High Dose 150 mg/kg bw |
male |
19.01 mg/L (30 min) |
5.54 mg/l (31 min) |
72.32 |
51.23 |
female |
9.64 mg/L (30 min) |
12.02 mg/l (88 min) |
71.89 |
81.81 |
Maximum concentrations of first sampling males > females
Maximum concentrations of second sampling females > males
=> The tetrahydronaphthalene blood concentration maximum was reached
approximately 30 minutes after administration of the highest dose.
AUC of second sampling always lower with males, higher with females as
compared to first sampling
=> The AUC of the high dose groups is more than proportional higher than that
of the lower dose groups indicating that elimination may be saturated at this dose level. An accumulation of test substance after
repeated oral administration of up to 150 mg/kg body weight was, however, not observed.
FIRST ORDER HALF LIVES OF ELIMINATION (1 compartment model)
high dose, male: 82.2 min
reversal, male: 99.5 min
high dose, female: 80.8 min
reversal, female: 85.0 min
FIRST ORDER HALF LIFE OF ELIMINATION (2 compartments model)
ca. 4.7 hours (males)
=> After 23 hrs, only traces of test substance were detectable in the blood. The elimination half life was determined in the range
of 30 to 100 minutes. In the low and mid dose groups, elimination was almost finished after 6 hours.
OTHER / GENERAL OBSERVATIONS:
Dark coloured urine was observed in all treated animals.
Tox. behaviour: see chapter 5.4
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
Resorption is rapid, but is probably decreased upon repeated dosing at high dose level. Excretion is rapid and complete. - Executive summary:
The present study describes the kinetics of tetrahydronaphthalene in male and female rats (five animals per dose per sex) at three dose levels (15, 50, and 150 mg/kg daily). Plasma concentration measurements were performed in the course of a subacute toxicity study of 28 days duration in an enriched study design. Two blood samples per animal were taken at different time points after application at day 1 and 16 (150 mg/kg daily) and at day 3 and 18 (15 and 50 mg/kg daily), respectively. Tetrahydronaphthalene was assayed by gas chromatography-mass spectrometry (GC-MS) after extraction. The data of plasma concentration time were analysed using non-linear mixed effects modelling as implemented in NONMEM. The structural model with the best fit employed one compartment kinetics with instantaneous drug input. Interindividual variability in both k and V was found to be very small [k, 0.201 h(-1), 0.013; V, 16.19 (kg), 1.77; population mean and SE]. No unequivocal evidence of dose dependence could be found. The kinetic parameter with the highest extent of variability was the extent of bioavailability which showed an coefficient of variation (CV) of 96%. Both gender and dose had no influence on the variability. The results of this study indicate that tetrahydronaphthalene is rapidly absorbed from the gastrointestinal tract and also rapidly excreted. Upon repeated application by gavage resorption was delayed at the highest dose level. There appears to be no induction of elimination upon repeated dosing. At higher dose level elimination is apparently saturated.
There was no accumulation upon repeated oral application of tetrahydronaphthalene up to 150 mg/kg bw.
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