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EC number: 210-258-8 | CAS number: 611-19-8
- 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:
- supporting study
- Study period:
- 2002-2003
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 003
- Report date:
- 2003
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5395 (In Vivo Mammalian Cytogenetics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- α,2-dichlorotoluene
- EC Number:
- 210-258-8
- EC Name:
- α,2-dichlorotoluene
- Cas Number:
- 611-19-8
- Molecular formula:
- C7H6Cl2
- IUPAC Name:
- 1-chloro-2-(chloromethyl)benzene
- Details on test material:
- Source: Clariant GmbH-Batch No. DEBG 047131-Purity: 99.6%
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harla Winkelmann GmbH, Borchen, Germany
- Age at study initiation: male/female animals appr. 6 weeks
- Weight at study initiation: male animals: 167 - 198 g (mean: 180.8 g); female animals: 137 - 159 g (mean: 145.4 g)
- Assigned to test groups randomly: yes
- Housing: 5 animals per macrolon cage type IV on soft wood granulate
- Diet: rat/mice diet ssniff R/M-H, ad libitum (ssniff GmbH, Soest, Germany)
- Water: tap water in platic bottles, ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 3
- Humidity (%): 50 +/- 20
- Air changes (per hr): air-conditioned room
- Photoperiod (hrs dark / hrs light): 12 /12
IN-LIFE DATES: From: 04-Feb 2002 To: 06-Feb 2002
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle/solvent used: sesame oil
- Justification for choice of solvent/vehicle: stability in the sovent
- Concentration of test material in vehicle: 5, 15, 50 mg/mL
- Amount of vehicle: 10mL/kg bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
One day before administration the test substance was dissolved in sesame oil at appropriate concentration. With regard to homogeneity, preparation was stirred until dosing had been completed. The positive control was dissolved in distilled water; final concentration: 4 mg/mL. - Duration of treatment / exposure:
- Twice at an interval of 24 hours (except positive control with only one dose)
- Frequency of treatment:
- see "Duration of treatment / exposure"
- Post exposure period:
- 24 h
Doses / concentrations
- Remarks:
- Doses / Concentrations:
50, 150, 500 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Endoxan R (cyclophosphamide)
- Route of administration: oral
- Doses / concentrations: 40 mg/kg bw
Examinations
- Tissues and cell types examined:
- Polychromatic erythrocytes gained from femoral bone marrow.
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
Preliminary dose-range finding study; test item was applied to 3 males and 3 females at a dose of (i) 600, (ii) 400, and (iii) 500 mg/kg bw. Oral administration of 600 mg/kg bw resulted in mortality in one male and two female rats. No macroscopic findings were observed and as clinical signs decreased motor activity and cowering posture were noticed at all doses. Highest sublethal dose of 500 mg/kg bw was selected for the main study.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields):
DETAILS OF SLIDE PREPARATION:
Femoral bone marrow was extracted, suspended in fetal bovine serum and centrifuged. Supernatant was discarded and drops of mixed sediment were smeared onto slides. Slides were stained with May-Grünwald's and Giemsa solution and finally coated.
METHOD OF ANALYSIS:
2000 polychromatic erythrocytes were counted per animal (number of cells with micronuclei was recorded). Additionally, the ratio of polychromatic erythrocytes to 200 normochromatic erythrocytes was determined. Main parameter for the statistical analysis was the proportion of polychromatic erythrocytes with micronuclei out of the 2000 counted erythrocytes. - Evaluation criteria:
- Proportion of polychromatic erythrocytes with micronuclei in the positive control is significantly higher than in the negative control (p<0.05).
A test substance producing no significant dose-related increase in the number of micronucleated polychromatic erythrocytes is considered as non-clastogenic. - Statistics:
- An one-sided Wilcoxon test was used. A significance level of 5 % was adopted for all tests.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- after twice oral administration of 500 mg/kg bw
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- see below
Any other information on results incl. tables
Oral administration of 500 mg/kg bw resulted in the death of
one male out of 10 animals treated. This animal was replaced
and survived after treatment. The following signs of toxicity
were observed in the main study from 2 hours to 6 hours after
the second application: diarrhea, stilted gait and cowering posture.
The dissection of the animals revealed no test substance
related macroscopic findings.
Animals from the other dose groups (50 mg/kg bw, 150 mg/kg
bw) showed neither clinical signs of toxicity nor
macroscopic findings after dissection.
The bone marrow smears were examined for the occurrence of
micronuclei in red blood cells. The results are summarized
in Table 1.
The incidence of micronucleated polychromatic erythrocytes
in the dose groups with o-chlorobenzyl chloride (OCBC) was
within the normal range of the negative control groups (mean
of micronucleated polychromatic erythrocytes per 2000 cells:
1.7 -4.9). No statistically significant increase in
micronucleated polychromatic erythrocytes was observed.
The ratio of polychromatic erythrocytes to total erythrocytes
in both male and female animals differed less than 20 % from
the control value in all dose groups, but decreased dose
dependently indicating slight toxicity in the highest dose group.
From the results, it was concluded that OCBC did not cause
a substantial increase in micronucleated polychromatic
erythrocytes and is not clastogenic in the micronucleus test
in vivo under the conditions described in this study.
Table 1.Results
========================================================
Sex Dose Poly/ Poly/ Poly Poly
(mg/kg bw) animal Ery with MN with MN
counted Mean Mean Mean [%]
--------------------------------------------------------
male 0-control 2000 0.47 3.0 0.15
male 50 2000 0.54 4.0 0.20
male 150 2000 0.51 3.2 0.16
male 500 2000 0.43 2.8 0.14
male 40-Endoxan 2000 0.46 30.8* 1.54
--------------------------------------------------------
female 0-control 2000 0.49 3.0 0.15
female 50 2000 0.50 3.0 0.15
female 150 2000 0.50 3.2 0.16
female 500 2000 0.41 3.2 0.16
female 40-Endoxan 2000 0.40 22.8* 1.14
=======================================================
*= significantly different from control (p<0.05)
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
- Executive summary:
In a bone marrow micronucleus assay Sprague-Dawley rats were treated orally with o-Chlorobenzylchloride (99.6 % a.i.); the vehicle was sesame oil. The micronucleus assay in male and female rats was conducted according to OECD TG 474 in compliance with GLP. A preliminary experiment showed that no death occurred at doses of 400 and 500 mg/kg bw while death (one out of three males and two out of three females) was observed at 600 mg/kg bw. Thus o-Chlorobenzylchloride was orally administered twice at an interval of 24 hours to the animals at 0, 50, 150 and 500 mg/kg bw. There were signs of toxicity in the dose group of 500 mg/kg bw: one out of ten animals died and the following clinical signs were observed 2 to 6 hours after the second treatment: diarrhea, stilted gait and cowering posture. All animals were sacrificed 24 hours after the second treatment, bone marrow cells harvested and exmined for micronuclei. The positive control induced the appropriate response. No statistically significant increase in the micronucleated polychromatic erythrocyte frequencies was observed in any dose groups, indicating that o-Chlorobenzylchloride is not clastogenic in vivo.
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