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EC number: 203-464-4 | CAS number: 107-12-0
- 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:
- genetic toxicity in vivo, other
- Remarks:
- aneuplody in Drosophila
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1991
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
Data source
Reference
- Reference Type:
- publication
- Title:
- Aneuploidy in Drosophila, IV. Inhalation studies on the induction of aneuploidy by nitriles
- Author:
- Osgood, C.
Bloomfield, M.
Zimmering, S. - Year:
- 1 991
- Bibliographic source:
- Osgood, C., Bloomfield, M. & Zimmering, S., 1991. Aneuploidy in Drosophila, IV. Inhalation studies on the induction of aneuploidy by nitriles. Mutation Research/Genetic Toxicology, 259(2), pp.165–176.
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The Drosophila ZESTE system was used to monitor the induction of sex chromosome aneuploidy following inhalation exposure of adult females to proplonitrile
- GLP compliance:
- not specified
- Type of assay:
- other: Drosophila aneuplody test
Test material
- Reference substance name:
- Propiononitrile
- EC Number:
- 203-464-4
- EC Name:
- Propiononitrile
- Cas Number:
- 107-12-0
- Molecular formula:
- C3H5N
- IUPAC Name:
- propanenitrile
Constituent 1
- Specific details on test material used for the study:
- Test chemicals were supplied by Radian Corpo- ration (Dallas, TX).
Test animals
- Species:
- Drosophila melanogaster
- Strain:
- not specified
- Details on species / strain selection:
- test females are of the genotype y z/y2 z f YL; spa(pol)
Adult females are mated with males of the genotype attached-X-Y, w; net. - Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- The standard chemical-treatment protocol em-
ployed adult females aged 2-3 days at the time of exposure (departures from tins protocol are de- scribed m Results). The females were lightly etherized and then transferred into 30-ml serum bottles capped with a rubber septum, 20 animals per bottle. When these fhes had fully recovered from etherlzation, 5 ~1 of appropriately diluted chemacal were spotted onto 0.5-cm diameter glass fiber filters which were lmmedmtely dropped into the serum bottles and the bottles capped with a septum and sealed with an aluminum collar. At the indicated time points, the bottles were un- capped and the flies shaken into empty glass vials for recovery.
Administration / exposure
- Route of administration:
- inhalation: vapour
- Details on exposure:
- It should be noted that the reported test concentrations may over- estimate the presented dose. In calculations of dose, we assumed that all the applied chemical volatilized w~thin the treatment period. To the extent that we could assess tins wsually, tins seemed to be the case as the treatment filters appeared completely dry within nunutes of their introduction into the treatment bottles. We as- sumed that the chermcals dispersed evenly within the air volume of the bottle (30 ml) and calculated the dose accordingly. Attempts to quantify the concentrations using gas chromatography were unsuccessful, because the chromatograph was not sufficiently sensitive to detect the low concentra-
tions used in these experiments.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 10 ppm (nominal)
- Dose / conc.:
- 30 ppm (nominal)
- Dose / conc.:
- 50 ppm (nominal)
- Dose / conc.:
- 70 ppm (nominal)
- No. of animals per sex per dose:
- 20
- Control animals:
- yes, concurrent no treatment
- Positive control(s):
- none
Examinations
- Evaluation criteria:
- At the indicated time points, the bottles were un- capped and the flies shaken into empty glass vials for recovery. The paralyzing effects and time for recovery varied between chemicals and treatment times. The recovered females were then shaken into bottles with w; net males (20 of each sex per bottle) and permitted to deposit eggs for two days (Brood A), transferred to fresh bottles for a second two-day sampling (Brood B) and then discarded. F1 offspring were counted and scored for exceptions on days 10 through 17 following the establishment of a brood.
- Statistics:
- Statistical analyses of the data were carried out as described previously (Margohn et al., 1983; Zimmering et al., 1990).
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- positive
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Positive controls validity:
- not examined
- Additional information on results:
- Propionltrlle was tested at 51 ppm and was found to induce aneuploidy after 50- and 70-mm exposures. Approximately equal numbers of chro- mosome gain and chromosome loss were re- covered when one examines the data pooled over time points. As was the case with acetonitnle, toxicity (45%) and sterility were induced by the 70-mm exposure, and the majority of exceptional offspring were recovered in Brood A. Proptonltrlle similarly induced a "knock-out" effect; approxi- mately 10 min were required to paralyze all animals at the presented dose of 51 ppm.
Any other information on results incl. tables
Virtually all exceptional offspring induced by acetonitrile and propionitnle were recovered in the first sampled eggs, corresponding to treated mature oocytes. Additionally, the time interval between treatment and sampling was shown to be important, suggesting rap~d loss or detoxifica- tion of the nltriles. Genetic analysis demonstrated that most aneuploids resulted from induced segregation errors during the first division of meiosis.
Whatever the cellular target(s) for the nitrlles may be in VlVO, it is clear that Drosophila is remarkably sensitive to this class of chemicals. In part this may reflect the fact that files freely inhale chemicals in the air through their spiracles, which In turn branch into extensive networks of trachea and trachioles that reach all cells, including those of the germline (Nikam and Khole, 1989). The extremely low doses that are effective in this orgamsm suggest an easily saturated cellular target the nature of which is unknown. Nxtriles are gen- erally weakly active in conventional genotoxlclty assays (Lambotte-Vandepaer and Duverger-van Bogaert, 1984; Galloway and Ivett, 1986). Thus, the ability to detect aneuploldy Induction by this class of chemicals underscores the importance of aneuploidy test systems.
Applicant's summary and conclusion
- Conclusions:
- The Drosophila ZESTE system was used to monitor the induction of sex chromosome aneuploidy following inhalation exposure of adult females to four nitriles: acetonltrile, proplonitrile, acrylomtrde and fumaromtnle. Propionitrlle was a highly effective aneuploidogen, inducing both chromosome loss and chromosome gain following brief exposures to low concentrations of these chemicals, and this nitrile also induced rapid paralysis.
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