Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 201-487-4 | CAS number: 83-56-7
- 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

Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2004-07-14 to 2005-04-25
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2005
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- 1997
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian bone marrow chromosome aberration test
Test material
- Reference substance name:
- Naphthalene-1,5-diol
- EC Number:
- 201-487-4
- EC Name:
- Naphthalene-1,5-diol
- Cas Number:
- 83-56-7
- Molecular formula:
- C10H8O2
- IUPAC Name:
- naphthalene-1,5-diol
- Reference substance name:
- unknown
- Molecular formula:
- none
- IUPAC Name:
- unknown
Constituent 1
impurity 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Details on species / strain selection:
- The mouse is an animal which has been used for many years as suitable experimental animal in cytogenetic investigations. There are many data available from such investigations which may be helpful in the interpretation of results from the micronucleus test. In addition, the mouse is an experimental animal in many physiological, pharmacological and toxicological studies. Data from such experiments also may be useful for the design and the performance of the micronucleus test
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Strain: NMRI
Source: RCC Ltd., Animal Breeding Services; CH-4414 Füllinsdorf
Number of animals: 90 (54 males/36 females)
Initial age at start of acclimatization: Males: 5 - 8 weeks
Females: 7 - 10 weeks
Acclimatisation: minimum 5 days
Initial Body Weight at Start of Treatment: males mean value 36.0 g (SD ± 1.8 g)
females mean value 36.0 g (SD ± 1.9 g)
According to the suppliers assurance the animals were in healthy condition. The animals were under quarantine in the animal house of RCC - CCR for a minimum of five days after their arrival. During this period the animals did not show any signs of illness or altered behaviour.
The animals were distributed into the test groups at random and identified by cage number.
Husbandry
The animals were kept conventionally. The experiment was conducted under standard laboratory conditions.
Housing: single
Cage Type: Makrolon Type I, with wire mesh top (EHRET GmbH, D-79302 Emmendingen)
Bedding: granulated soft wood bedding
(Harlan Winkelmann GmbH, D-33178 Borchen)
Feed: pelleted standard diet, ad libitum
(Harlan Winkelmann GmbH, D-33178 Borchen)
Water: tap water, ad libitum, (Gemeindewerke, D-64380 Roßdorf)
Environment: temperature 22 ± 3 °C
relative humidity 30 - 83 % artificial light 6.00 a.m. - 6.00 p.m.
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- The test item was formulated in aqueous DMSO (30%). The vehicle was chosen to its relative non-toxicity for the animals.
- Details on exposure:
- Pre-Experiment for Toxicity
A preliminary study on acute toxicity was performed with two animals per sex under identical conditions as in the mutagenicity study concerning: animal strain; vehicle; route, frequency, and volume of administration.
The animals were treated i.p. with the test item and examined for acute toxic symptoms at intervals of around 1 h, 2-4 h, 6 h, 24 h, 30 h, and 48 h after administration of the test item.
Dose Selection
It is generally recommended to use the maximum tolerated dose or the highest dose that can be formulated and administered reproducibly or 2000 mg/kg as the upper limit for non-toxic test items.
The maximum tolerated dose level is determined to be the dose that causes toxic reactions without having major effects on survival within 48 hours.
The volume to be administered should be compatible with physiological space available.
Three adequate spaced dose levels spaced by a factor of 2 were applied at the central sampling interval 24 h after treatment. For the highest dose level an additional sample was taken at 48 h after treatment.
Study Procedure
Test Groups:
Six males and six females were assigned to each test group.
Treatment:
At the beginning of the treatment the animals (including the controls) were weighed and the individual volume to be administered was adjusted to the animals body weight. The animals received the test item, the vehicle or the positive control substance once. Twelve animals, six males and six females, were treated per dose group and sampling time.
Analysis of the Test Item Concentration in Blood
In order to quantify the concentration of the test item in blood 3 additional males per sampling interval were treated with 50 mg test item/kg b.w. intraperitoneally. 20 and 40 minutes as well as 1 and 4 hours after the treatment, the animals were sacrificed and their blood was collected and stored at – 80 °C until shipment on dry ice to the sponsor (Henkel KGaA,VTF-HSA, Henkelstraße 67, D-40191 Düsseldorf). Due to a technical error (no anti- coagulant was added to the blood samples), this part of the experiment had to be repeated.
The test item concentration in the blood samples was analysed in a separate study by the sponsor. - Duration of treatment / exposure:
- The animals received the test item, the vehicle or the positive control substance once.
- Frequency of treatment:
- The animals received the test item, the vehicle or the positive control substance once.
- Post exposure period:
- The animals of the highest dose group were examined for acute toxic symptoms at intervals of around 1 h, 2-4h, 6 h and 24 h after administration of the test item.
Sampling of the bone marrow was done 24 and 48 hours after treatment, respectively.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 50 mg/kg bw/day (nominal)
- Remarks:
- On the basis of 8 pre-exepriments, 50 mg/kg b.w. were estimated to be suitable as the high dose. The volume administered was 10 mL/kg b.w.
- Dose / conc.:
- 25 mg/kg bw/day (nominal)
- Remarks:
- The volume administered was 10 mL/kg b.w.
- Dose / conc.:
- 12.5 mg/kg bw/day (nominal)
- Remarks:
- The volume administered was 10 mL/kg b.w.
- No. of animals per sex per dose:
- In the main experiment for the highest dose group 24 animals (12 males, 12 females) received i.p. a single dose of 50 mg/kg b.w. of naphthalene-1,5-diol formulated in aqueous DMSO (30%) .
For the mid dose group 12 animals (6 males, 6 females) received i.p. a single dose of 25 mg/kg b.w. naphthalene-1,5-diol formulated in aqueous DMSO (30%).
For the low dose group 12 animals (6 males, 6 females) received i.p. a single dose of 12.5 mg/kg b.w. naphthalene-1,5-diol formulated in aqueous DMSO (30%) .
The volume administered was 10 mL/kg b.w.. - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Name: CPA; Cyclophosphamide
Supplier: Sigma-Aldrich Vertriebs GmbH
82041 Deisenhofen
Catalogue no.: C 0768 (purity: > 98%)
Dissolved in: deionised water
Dosing: 40 mg/kg b.w.
Route and frequency of administration: intraperitoneally, once
Volume administered: 10 mL/kg b.w.
Solution prepared on day of administration.
The stability of CPA at room temperature is sufficient. At 25°C only 3.5 % of its potency is lost after 24 hours (7).
Examinations
- Tissues and cell types examined:
- The animals were anaesthetised with CO2 and sacrificed by cervical dislocation. The femora were removed, the epiphyses were cut off and the marrow was flushed out with fetal calf serum, using a syringe. The cell suspension was centrifuged at 1500 rpm (390 x g) for 10 minutes and the supernatant was discarded.
- Details of tissue and slide preparation:
- A small drop of the resuspended cell pellet was spread on a slide. The smear was air-dried and then stained with May-Grünwald (MERCK, D-64293 Darmstadt)/Giemsa (Gurr, BDH Limited Poole, Great Britain). Cover slips were mounted with EUKITT (KINDLER, D-79110 Freiburg). At least one slide was made from each bone marrow sample.
- Evaluation criteria:
- Evaluation of the slides was performed using NIKON microscopes with 100x oil immersion objectives. At least 2000 polychromatic erythrocytes (PCE) were analysed per animal for micronuclei. To describe a cytotoxic effect the ratio between polychromatic and total erythrocytes was determined in the same sample and expressed in polychromatic erythrocytes per 2000 erythrocytes. The analysis was performed with coded slides.
Ten animals (5 males, 5 females) per test group were evaluated as described. The remaining 6th animal of each sex is usually evaluated in case an animal dies in its test group spontaneously.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
Any other information on results incl. tables
Toxic Symptoms in the Main Experiment
In the main experiment for the highest dose group 24 animals (12 males, 12 females) received i.p. a single dose of 50 mg/kg b.w. A 018 formulated in aqueous DMSO (30%) . The volume administered was 10 mL/kg b.w..
The animals treated with 50 mg/kg b.w. expressed toxic reactions as shown in the table:
Toxic
Reactions |
hours post-treatment hours post-treatment male / female |
||||
1 h |
2-4 h |
6 h |
24 h |
48 h* |
|
reduction of spontaneous activity |
12/12 |
12/12 |
12/12 |
12/9 |
3/2 |
abdominal position |
12/12 |
12/12 |
12/12 |
0/0 |
0/0 |
ruffled fur |
12/12 |
12/12 |
12/12 |
12/5 |
2/1 |
apathy |
1/2 |
0/0 |
0/0 |
0/0 |
0/0 |
*: data only from 6 animals per sex.
For the mid dose group 12 animals (6 males, 6 females) received i.p. a single dose of 25 mg/kg b.w. A 018 formulated in aqueous DMSO (30%) . The volume administered was 10 mL/kgb.w..
The animals treated with 25 mg/kg b.w. expressed toxic reactions as shown in the table:
toxic reactions |
hours post-treatment male / female |
|||
1 h |
2-4 h |
6 h |
24 h |
|
reduction of spontaneous activity |
6/6 |
6/6 |
6/6 |
4/3 |
abdominal position |
1/2 |
4/5 |
3/2 |
0/0 |
ruffled fur |
5/6 |
6/6 |
6/6 |
4/3 |
For the low dose group 12 animals (6 males, 6 females) received i.p. a single dose of
12.5 mg/kg b.w. A 018 formulated in aqueous DMSO (30%) . The volume administered was 10 mL/kg b.w..
The animals treated with 12.5 mg/kg b.w. expressed toxic reactions as shown in the table:
toxic reactions |
hours post-treatment male / female |
|||
1 h |
2-4 h |
6 h |
24 h |
|
reduction of spontaneous activity |
2/3 |
6/6 |
6/6 |
4/3 |
ruffled fur |
3/2 |
3/3 |
1/2 |
2/1 |
Summary of Micronucleus Test Results
test group |
dose mg/kg b.w. |
sampling time (h) |
PCEs with micronuclei (%) |
range |
PCE per 2000 erythrocytes |
vehicle |
0 |
24 |
0.105 |
0 -4 |
1099 |
test item |
12,5 |
24 |
0.080 |
0 -4 |
1124 |
test item |
25 |
24 |
0.105 |
0 -4 |
1096 |
test item |
50 |
24 |
0.080 |
0 -4 |
1082 |
positive control |
40 |
24 |
2.270 |
20 -76 |
1035 |
test item |
50 |
48 |
0.090 |
0 -4 |
1089 |
Biometry
Statistical significance at the five per cent level (p < 0.05) was evaluated by means of the non-parametric Mann-Whitney test.
Vehicle control versus test group |
Significance |
p |
12.5 mg A 018/kg b.w.; 24 h |
n.t. |
- |
25 mg A 018/kg b.w.; 24 h |
n.t. |
- |
50 mg A 018/kg b.w.; 24 h |
n.t. |
- |
40 mg CPA/kg b.w.; 24 h |
+ |
< 0.0001 |
50 mg A 018/kg b.w.; 48 h |
n.t. |
- |
- = not significant
+ = significant;
n.t = not tested, as the mean micronucleus frequency was not above the vehicle controlvalue
Applicant's summary and conclusion
- Conclusions:
- A test item is classified as mutagenic if it induces either a dose-related increase or a clear increase in the number of micronucleated polychromatic erythrocytes in a single dose group. Statistical methods (nonparametric Mann-Whitney test (8)) will be used as an aid in evaluating the results. However, the primary point of consideration is the biological relevance of the results.
A test item that fails to produce a biological relevant increase in the number of micronucleated polychromatic erythrocytes is considered non-mutagenic in this system.
In conclusion, it can be stated that during the study described and under the experimental conditions reported, the test item did not induce micronuclei as determined by the micronucleus test in the bone marrow cells of the mouse. - Executive summary:
The test item naphthalene-1,5-diol was assessed in the micronucleus assay for its potential to induce micronuclei in polychromatic erythrocytes (PCE) in the bone marrow of the mouse.
The test item was formulated in aqueous DMSO (30%) , which was also used as vehicle control. The volume administered i.p. was 10 mL/kg b.w.. 24 h and 48 h after a single administration of the test item the bone marrow cells were collected for micronuclei analysis.
Ten animals (5 males, 5 females) per test group were evaluated for the occurrence of micronuclei. At least 2000 polychromatic erythrocytes (PCEs) per animal were scored for micronuclei.
To describe a cytotoxic effect due to the treatment with the test item the ratio between polychromatic and total erythrocytes was determined in the same sample and reported as the number of PCEs per 2000 erythrocytes.
The following dose levels of the test item were investigated:
24 h preparation interval: 12.5, 25 and 50 mg/kg b.w.. 48 h preparation interval: 50 mg/kg b.w..
As estimated by pre-experiments 50 mg naphthalene-1,5-diol per kg b.w. was the highest applicable dose without significant effects on the survival rates. At this dose the animals showed clear signs of toxicity. At a higher dose (75 mg/kg) one male and one female animal died.
The mean number of polychromatic erythrocytes was not decreased after treatment with the test item as compared to the mean value of PCEs of the vehicle control indicating that A 018 had no cytotoxic properties in the bone marrow. The analysis of the blood samples of the males (see annex 2) treated with 50 mg test item /kg b.w. showed, that the test item could be quantified in the blood of the treated animals only in the blood samples taken 20 minutes after the treatment (2.5, 1.0 and 0.5 µg/mL). The samples from the later time points did not contain any quantifiable levels of the test item (data of the 1 and 4 h samplings not included). Thus, the bioavailability of the test item could be confirmed.
In comparison to the corresponding vehicle controls there was no statistically significant or biologically relevant enhancement in the frequency of the detected micronuclei at any preparation interval and dose level after administration of the test item. The mean values of micronuclei observed after treatment with naphthalene-1,5-diol were below or near to the value of the vehicle control group.
40 mg/kg b.w. cyclophosphamide administered i.p. was used as positive control which showed a statistically significant increase of induced micronucleus frequency.
In conclusion, it can be stated that during the study described and under the experimental conditions reported, the test item did not induce micronuclei as determined by the micronucleus test in the bone marrow cells of the mouse.
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.
