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EC number: 202-051-6 | CAS number: 91-22-5
- 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
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- No data
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: No guideline followed but the study is similar to the OECD 474 guideline. Only one sex was tested but quinoline shows carcinogenicity in male and females.
Data source
Reference
- Reference Type:
- publication
- Title:
- Effects of quinoline and 8-hydroxyquinoline on mouse bone marrow erythrocytes as measured by the micronucleus assay.
- Author:
- Hamoud MA, Ong T, Petersen M, Nath J
- Year:
- 1 989
- Bibliographic source:
- Teratogenesis, carcinogenesis and mutagenesis 9: 111-118
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- No guideline available when the study was performed.
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Quinoline
- EC Number:
- 202-051-6
- EC Name:
- Quinoline
- Cas Number:
- 91-22-5
- Molecular formula:
- C9H7N
- IUPAC Name:
- quinoline
- Details on test material:
- Supplier Radian Corp (Austin).
No further information
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding lab (USA)
- Age at study initiation: 6 to 8 weeks
- Weight at study initiation: no data
- Assigned to test groups randomly: no data
- Fasting period before study: no data
- Housing: 5 per cage, bedding consisted of hardwood chips and excelsior nesting material.
- Diet: Purina laboratory rodent chow, ad libitum
- Water : ad libitum
- Acclimation period: 5-7 days
ENVIRONMENTAL CONDITIONS
no data
IN-LIFE DATES: no data
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: corn oil
- Justification for choice of solvent/vehicle: no data
- Concentration of test material in vehicle: 2.5; 5 or 10 mg/mL
- Amount of vehicle : 10 mL/kg
- Lot/batch no. (if required): no data
- Purity: no data - Details on exposure:
- Single injection by ip
- Duration of treatment / exposure:
- Single dose
- Frequency of treatment:
- Single dose
- Post exposure period:
- 24, 48 or 72 h
Doses / concentrations
- Remarks:
- Doses / Concentrations:
25, 50 and 100 mg/kg
Basis:
nominal conc.
- No. of animals per sex per dose:
- 15 animals per dose, only males
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- triethylenemelamine
- Justification for choice of positive control(s): no data
- Route of administration: ip
- Doses / concentrations: 0.5 mg/kg in phosphate buffered saline
Examinations
- Tissues and cell types examined:
- Bone marrow
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
Based on a SCE study
DETAILS OF SLIDE PREPARATION:
4 replicate slides were prepared for each animal.
Overnight air-dried smears were fixed for 15 min in absolute methanol and stained by using May-Gruenwald-Giemsa staining technique
METHOD OF ANALYSIS:
No data
- Evaluation criteria:
- 2000 polychromatic erythrocytes (PCE) per animal were scored for the presence of micronuclei (MN).
As measurement of the toxic effect to erythropoietic tissue, the PCE normochromatic erythrocytes (NCE) ratios were calculated by scoring the number of NCE encountered during the screening of the first 1000 PCE.
A PCE (or NCE) with micronucleus, regardless of the number, was counted as one MPCE (or MNCE). - Statistics:
- two-tailed Student's t-test to compare MPCE values between treated and control animals.
The Cochran-Armitage two-tailed trend test was used to determine the dose-response relationship.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- positive
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Positive controls validity:
- not specified
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
No range finding, dosing based on a SCE study
Any other information on results incl. tables
Sampling time (h) |
Dose (mg/kg) |
MPCE / 1000 PCE +/- S.D.a |
PCE/NCEb |
24 |
0 |
3.0 +/- 0.3 |
0.82 |
25 |
4.7 +/- 0.5* |
0.69 |
|
50 |
9.2 +/- 1.7** |
0.61 |
|
100 |
12.5 +/- 1.7** |
0.79 |
|
48 |
25 |
3.9 +/- 0.2 |
0.82 |
50 |
7.0 +/- 0.5** |
1.08 |
|
100 |
8.3 +/- 0.5** |
1.04 |
|
72 |
25 |
2.8 +/- 0.4 |
1.33 |
50 |
2.5 +/- 0.4 |
1.27 |
|
100 |
3.0 +/- 0.6 |
1.08 |
|
24c |
0 |
2.4 +/- 0.3 |
0.85 |
25 |
4.9 +/- 0.4** |
0.69 |
|
50 |
6.9 +/- 0.3** |
0.72 |
|
100d |
7.9 +/- 0.6** |
0.75e |
aTotal MPCE/10 000 PCE (2 000 PCE were scored for each of 5 animals)
bBased on 5 000 PCE
cResult from repeat experiment
dOnly 4 animals were analyzed
eBased on 4 000 PCE
* P< 0.05
** P < 0.01
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): positive
Quinoline induced micronucleus in bone marrow cells of the mice treated by ip injection. - Executive summary:
An in vivo micronucleus test has been performed on mice, treated with quinoline at 25, 50 and 100 mg/kg by single ip injection. The animals were sacrificed at 24, 48 and 72 h after treatment and the bone marrow was sampled and analysed.
The experiment was repeated with the same concentrations but with a sampling at 24 h only.
In these conditions, quinoline induced micronucleus in the erythrocytes.
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