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EC number: 201-152-2 | CAS number: 78-87-5
- 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 germ cell study: cytogenicity / chromosome aberration
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- May 15, 1989
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted according to EPA TSCA guidelines and in accordance with GLP.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 989
- Report date:
- 1989
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EPA OTS 798.5450 (Rodent Dominant Lethal Assay)
- Principles of method if other than guideline:
- no data
- GLP compliance:
- yes
- Type of assay:
- rodent dominant lethal assay
Test material
- Reference substance name:
- 1,2-dichloropropane
- EC Number:
- 201-152-2
- EC Name:
- 1,2-dichloropropane
- Cas Number:
- 78-87-5
- Molecular formula:
- C3H6Cl2
- IUPAC Name:
- 1,2-dichloropropane
- Details on test material:
- - Name of test material (as cited in study report): Propylene Dichloride
- Physical state: colourless liquid
- Analytical purity: 99.9 %
- Lot/batch No.: TB871112/TB072088
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: Charles River Breeding Laboratories
- Age at study initiation: Males - 4 weeks when purchased, females - 10 weeks when purchased
- Assigned to test groups randomly: [yes, under following basis: stratified by weight and randomly assigned to treatment and control groups]
- Housing: group housed in stainless steel cages during cohabitation, else PDC treated males housed in plastic shoe box cages with ground cob nesting naterial and animals of the positive control group housed in stainless steel cages
- Diet (e.g. ad libitum): ad libitum Purina Certified Rodent Chow no.5002
- Water (e.g. ad libitum): ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): standard conditions
- Humidity (%): standard conditions
- Air changes (per hr): standard conditions
- Photoperiod (hrs dark / hrs light): standard conditions
IN-LIFE DATES: not specified in the report
Administration / exposure
- Route of administration:
- oral: drinking water
- Vehicle:
- not applicable
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: PDC was administered continuously in the drinking water at concentrations of 0, 0.024%, 0.10% and 0.24% (w/v) to groups of 30 male rats. Test solutions were prepared by diluting the test material with tap water, according to in-house SOP's. Test solutions were administered in 9" x 9", 1.6 liter capacity, sealed Tedlar Gas and Water Sampling Bags with a modified 1/4" diameter Jaco Kynar bulkhead union fitted with a pressure-activated stainless steel nipple, to prevent any loss due to evaporation. Test solutions were mixed and changed at least weekly. The bags were changed weekly and autoclaved between uses.
- Duration of treatment / exposure:
- 14 weeks
- Frequency of treatment:
- Daily and continuous
- Post exposure period:
- 2 weeks
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0 %
Basis:
nominal in water
analytical - not detected
- Remarks:
- Doses / Concentrations:
0.024 %
Basis:
nominal in water
analytical - 0.0211 ± 13 %
- Remarks:
- Doses / Concentrations:
0.10 %
Basis:
nominal in water
analytical - 0.098 ± 90 %
- Remarks:
- Doses / Concentrations:
0.24 %
Basis:
nominal in water
analytical - 0.2411 ± 240 %
- No. of animals per sex per dose:
- 30 males - treated mated with naive (untreated) adult virgin females over a period of two weeks, during which each male was cohabited with two naive females/week.
- Control animals:
- yes
- Positive control(s):
- Cyclophosphamide
- Justification for choice of positive control(s): known positive control agent recommended by various guidelines and regulatory agencies
- Route of administration: per oral
- Doses / concentrations: 100 mg of cyclophosphamide/kg body weight
Examinations
- Tissues and cell types examined:
- Gross pathological observations conducted
- Details of tissue and slide preparation:
- not applicable
- Evaluation criteria:
- A test substance which does not produce either a statistically significant dose-related increase in the number of dominant lethals or a statistically significant and reproducible positive response at any one of the test points is considered nonmutagenic in this assay/test.
- Statistics:
- Body weight data analysed by Bartlett's test, ANOVA, Dunnett's test or Wilcoxon Rank_Sum Test with Bonferroni's correction
Feed and water consumption data evaluated by descriptive statistics, outliers identified by Grubb's method and excluded from analysis
Fetility indices analysed by Fischer exact probability test.
The numbers of corpora lutea and implantation analysed by ANOVA and Wilcoxon Rank-Sum Test
Pre-implantation losses and resorption rates analysed by modifed Wilcoxon test
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- not applicable
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Refer to Tables 2- for detailed information
Any other information on results incl. tables
None
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Propylene dichloride was not considered mutagenic following a dominant lethal assay in which male Sprague Dawley rats were exposed to drinking water concentrations of 0.024 %, 0.10 % and 0.24 % (w/v) for 14 weeks. At these concentrations, water consumption was depressed in a dose-dependent manner, and body weights were decreased by 0.10 % and 0.24 %. Cyclophospahmide (100 mg/kg single oral dose), a known mutagen, induced a significant dominant lethal effect in the study. - Executive summary:
The mutagenic potential of Propylene dichloride (PDC) was evaluated in the dominant lethal assay in groups of 30 male Spargue-Dawley rats exposed to PDC in drinking water at concentrations of 0, 0.024%, 0.10% and 0.24% (w/v) continuously for a period of 14 weeks as part of a combined reproduction/dominant lethal study. (These concentrations corresponded to time-weighted average daily doses of approximately 0, 28, 91 and 162 mg PDC/kg body weight/day). Exposed males were then mated to pairs of naive, untreated adult females for two successive periods of one week each. A separate, positive control group of 30 male Sprague-Dawley rats were administered a single oral dose of 100 mg cyclophosphamide/kg body weight 48-hours prior to breeding with untreated females. The uterine contents of these females were then evaluated for evidence of a dominant lethal effect as manifested by an increase in the resorption rate.
Among PDC-treated males, concentration-related decreases in water consumption were noted at all levels treated and decreased body weights were noted in males given 0.10% and 0.24% in the water. Mating performance was unaffected in these animals. Evaluation of the resorption rates among these groups revealed that the weekly values for the females mated to PDC-treated males ranged from 2.2% to 8.1%, well within the historical control range. Resorption rates among the concurrent controls were low, ranging from 3.5% to 5.4%. Statistically significant increases from concurrent control values identified during the first week of breeding in the resorption rates in the 0.024% and 0.24% PDC-treated groups were considered within the normal limits. In contrast, single oral administration of cyclophosphamide at a dose of 100 mg/kg resulted in a 10-fold increase in the resorption rate, consistent with the reported values. The concentrations of PDC in the drinking water were at the limit of solubility in water and were approximately 10000-fold higher than levels detected in the environment. Despite these exaggerated levels, PDC was not nutagenic in this dominant lethal assay in male Sprague-Dawley rats exposed continuously to concentrations up to 0.24% in the drinking water.
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