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EC number: 802-100-7 | CAS number: 1093653-57-6
- 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 / bone marrow chromosome aberration
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP compliant guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 475 (Mammalian Bone Marrow Chromosome Aberration Test)
- GLP compliance:
- yes
- Type of assay:
- chromosome aberration assay
Test material
- Reference substance name:
- 4-(heptyloxy)-3-methylbutanal
- EC Number:
- 802-100-7
- Cas Number:
- 1093653-57-6
- Molecular formula:
- C12H24O2
- IUPAC Name:
- 4-(heptyloxy)-3-methylbutanal
- Test material form:
- other: liquid
- Details on test material:
- - Name of test material (as cited in study report): TM 09-217c
- Physical state: colourless liquid
- Storage condition of test material: ambient temperature and protected from light
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Animal Receipt and Acclimation
Virus antibody-free (VAF) mice were obtained from a supplier that monitored mice for evidence of ectoparasites, endoparasites, pathogenic bacteria, mycoplasmas, and appropriate murine viruses and were acclimatized for 5 or 7 days after receipt. At BioReliance, mice were observed each day for signs of illness and other conditions of poor health. All mice were judged to be healthy prior to utilization in the study.
Animal Welfare Provisions and Animal Care
This study is not duplicative or unnecessary. The number of mice and the procedures and experimental design used for this study have been reviewed and were approved by the BioReliance Institutional Animal Care and Use Committee #8 and #9. All procedures involving mice performed at BioReliance follow the specifications recommended in The Guide for the Care and Use of Laboratory Animals (National Academy Press, Washington, D.C., 2011).
Animals were housed in an AAALAC-accredited facility with a controlled environment of 50 ± 20% relative humidity, 72 ± 3°F temperature and a 12 hour light/dark cycle. The animal rooms were supplied with at least 10 changes of fresh HEPA-filtered air every hour.
Mice of the same sex were housed up to five per rodent Micro-Barrier cage. Cages were placed on the racks equipped with an automatic watering system and Micro-VENT full ventilation, HEPA filtered system. The purpose of this system was to supply uninterrupted positive air to each individual rodent Micro-Barrier cage and to capture the effluent air from each cage and re-filter the air (HEPA) prior to introducing the air back into the cage.
Heat-treated Sani-Chip hardwood chips were used for bedding to absorb liquids (P.J. Murphy Forest Products, Montville, NJ). Bedding was analyzed by the Manufacturer for any contaminants.
Animals were allowed free access to tap water, which meets U.S. EPA drinking water standards [water source is Washington Suburban Sanitary Commission (WSSC) Potomac Plant]. Drinking water was monitored at least annually for levels of specified microorganisms, pesticides, heavy metals, alkalinity and halogens.
A certified laboratory rodent chow (Harlan 2018C Certified Global Rodent Diet) was provided ad libitum. The food was analyzed by the manufacturer for the concentrations of specified heavy metals, aflatoxin, chlorinated hydrocarbons, organophosphates and specified nutrients.
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- Corn oil was used to deliver TM 09-217c to the test system based on the solubility of the test substance, compatibility with the test system and route of administration. Corn oil (CAS number: 8001-30-7, lot number: MKBD6671, expiration date: 24 September 2013) was obtained from Sigma-Aldrich. Corn oil is characterized as per the Certificate of Analysis on file with the Testing Facility.
- Details on exposure:
- The test substance dose formulations were prepared fresh for each phase of the study prior to dose administration. All formulations at concentrations, 3.125, 6.25, 12.5, 25, 35, 50, 62.5, 75, and 100 mg/ml in the DRF assay, and all formulations at concentrations 25, 50 and 100 mg/mL in the definitive study were prepared by combining an appropriate amount of test substance with an appropriate volume of the vehicle. Each formulation was vortexed for 1 minute and stirred for a total of 20 minutes using a stir bar/plate. All formulations appeared as yellow solutions and were stirred prior to and during dose administration.
All dose formulations were administered as single intraperitoneal injections (IP) at a dose volume of 20 mL/kg body weight. Intraperitoneal administration has been routinely used, and is widely-accepted route of administration for use in the mammalian bone marrow chromosome aberration assay.
In order to arrest the cells in metaphase, all main assay animals received a dose of 2 mg/kg of colchicine at ~ 3hours prior to bone marrow collection. Neat colchicine was diluted in Hank’s Balanced Salt solution (HBSS) at a concentration of 0.5 mg/mL and was intraperitoneally administered to the animals at a dose volume of 4 mL/kg body weight.
All mice in the experimental groups were weighed immediately prior to dose administration, and the administered volume was based on individual body weight. - Duration of treatment / exposure:
- All dose formulations were administered as single intraperitoneal injections (IP) at a dose volume of 20 mL/kg body weight.
- Frequency of treatment:
- single IP injection
- Post exposure period:
- three days
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Dose range finding assay: 62.5, 125, 250, 500, 700, 1000, 1250, 1500, or 2000 mg/kg. Definitive study:500, 1000 or 2000 mg/kg
Basis:
nominal conc.
- No. of animals per sex per dose:
- Dose range finding assay: 3 mice/sex/group
Definitive study: 5 mice/group (only males), additional 21 mice/group as satellite groups were assigned for the toxicolinetic portion of the study - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide monohydrate (CP, CAS number: 6055-19-2, lot number: 120M1253V, expiration date: 31 December 2013), obtained from Sigma – Aldrich, were used as positive control substance.
An aqueous dosing formulation of CP, at a concentration of 2.5 mg/mL, was prepared fresh on the day of dose administration. An appropriate amount of CP was dissolved in an appropriate volume of sterile water for injection (B. Braun Medical, CAS number: 7732-18-5, lot number: J12003, expiration date: September 2013). The accuracy of the preparation and stability of the CP formulation was demonstrated by acceptable results that met the criteria for a valid test.
5 mice were used in the positive control group.
Examinations
- Tissues and cell types examined:
- Bone marrow
- Details of tissue and slide preparation:
- Animals were administered colchicine intraperitoneally at ~ 3hours prior to scheduled bone marrow collection. At 18 ±0.5 hr or 42±0.5 hr post dose administration, and following colchicine treatment, mice were sacrificed by carbon dioxide asphyxiation (verified by toe pinch reflex) in the same sequence used for dosing. The femurs were exposed, cut just above the knee and bone marrow was aspirated into a syringe containing a small volume of HBSS. The bone marrow cell suspensions were transferred into appropriately labeled tubes containing 3 to 5 mL of HBSS. The tubes with bone marrow were kept on wet ice until centrifugation. The cells were collected by centrifugation (100 x g; 5-10 minutes; refrigerated centrifuge set at 4°C), re-suspended in 5 mL of warm (37°±1°C) hypotonic solution of 0.065M KCl, and then incubated for 10±1 minutes in water bath at 37°C±1°C to swell the cells. Following this incubation period, a few drops of fixative (methanol: acetic acid, 3:1 v/v) was added and the cells collected by centrifugation (100 x g; 5-10 minutes; refrigerated centrifuge). Following centrifugation, the supernatant was discarded and cell pellets were re-suspended. Fresh fixative (5 mL) was added to each tube, the tubes were centrifuged, supernatant was discarded and cell pellets were re-suspended. Following another change of fixative, centrifugation and re-suspension of cells, fresh fixative was added and the tubes were capped and stored overnight at 2°C to 8°C. To prepare slides, the cells were collected by centrifugation (100 x g; 5-10 minutes; refrigerated centrifuge) and re-suspended to opalescence in fresh fixative. Two to four drops of fixed cells were dropped onto a wet slide and air-dried. Each slide was identified by the study number and animal number. Two slides were prepared from each animal, air dried, stained with Giemsa stain and permanently mounted.
Slides were coded using a random number table by an individual not involved with the scoring process. Metaphase spreads (cells) were examined using a light microscope and under oil immersion (1000X) without prior knowledge of treatment groups.
The Mitotic Index (MI) was determined for each animal, across all treatment groups, and at both collection time points. The MI was determined as the percentage of cells in mitosis based upon 1000 cells counted per animal. The mean MI was calculated for each treatment group (including positive and negative control groups) and served as a parameter of cytotoxicity and inhibition of cell division.
A minimum of 100 metaphase spreads containing 40 chromosomes, were examined from each animal and scored for chromatid-type and chromosome-type aberrations. Fewer cells (50 metaphase spreads) were scored per animal in the cyclophosphamide group when a higher percentage of aberrations, i.e. >10%, is observed during the scoring.
The following structural aberrations were recorded:
Chromatid-type aberrations: chromatid and isochromatid breaks and exchange figures such as quadriradials (symmetrical and asymmetrical interchanges), triradials and complex rearrangements.
Chromosome-type aberrations: chromosome breaks and exchange figures such as dicentric chromosomes and rings.
Fragments observed with an exchange figure were not scored as an aberration but not considered part of the incomplete exchange.
Pulverized chromosome(s), pulverized cells and severely damaged cells (≥ 10 aberrations) were also recorded.
Chromatid and isochromatid gaps were recorded but not included in the analysis.
The XY coordinates for each cell with structural aberrations were recorded using a calibrated microscope stage.
The percent polyploid and endoreduplicated cells were determined per 100 metaphase cells per animal. - Evaluation criteria:
- All conclusions are based on the scientific judgment of generated data; however as a guide to the interpretation of the data, the following criteria are taken into consideration:
• The test substance is considered to induce a positive response if the percent of aberrant cells is significantly increased at one or more dose levels relative to the vehicle (negative) control at any sampling time (Fisher's exact test; p< 0.05).
• A dose-dependent increase is also taken into consideration in the determination of a test substance positive response.
• Values that are statistically significant but do not exceed the range of historical negative or vehicle controls (fall within or just outside the range) may be judged as not biologically significant or relevant, therefore, the test substance will be considered negative for the induction of chromosome aberrations in bone marrow cells.
• The test substance is judged negative if no statistically significant increase in the percent of aberrant cells is observed in the test substance groups relative to the concurrent negative (vehicle) control groups at any of the sampling times. - Statistics:
- Statistical analysis of the percentage of aberrant cells was performed using the Fisher's exact test (p< 0.05). The Fisher's exact test is used for pairwise comparisons of the percentage of aberrant cells between each test substance group and negative control group. In the event of a positive Fisher's exact test, the Cochran-Armitage test is used to evaluate the significance of a dose-response.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- Clinical Signs
No mortality was observed. All mice in the control substance groups and all mice in the 500 mg/kg treatment group appeared normal during the study period. Piloerection was observed in the 1000 and 2000 mg/kg treatment groups. In addition, lethargy was noted in the 2000 mg/kg treatment group
Bone Marrow Evaluation
Microscopic evaluation of bone marrow cells indicated the following:
Reductions in the Mitotic Index (MI) of 45%, 26%, and 21% were observed in the 500, 1000, and 2000 mg/kg treatment groups, respectively at 18 hour post-dose relative to the vehicle control group. A 53% reduction in the MI was noted in the 2000 mg/kg treatment group at 42 hours post-dose.
No statistically significant increases in the number of cells with structural aberrations compared to the vehicle control were noted in any of the test substance treatment groups (Fisher’s exact test; p> 0.05). In contrast, CP induced a statistically significant increase in the number of structurally -aberrant cells compared to the vehicle control (Fisher’s exact test; p< 0.05). No numerical aberrations were observed in any of the test substance groups or the control groups.
Dose Formulation Analysis
Aliquots of vehicle control and test substance formulations used in the dose administration were analyzed by BioReliance analytical chemistry department. The analyses were performed by gas chromatography (GC) using a method validated under BioReliance Study Number AD39TS.GCGTCHEM.BTL. The analysis results indicated the following:
No test substance was detected in the vehicle control sample.
All test substance formulations met the protocol specified acceptance criteria of 85.0% -115.0% of target concentrations and ≤5.0% relative standard deviation (%RSD).
Test substance formulations from the low and high concentrations were held at room temperature for 3.5 hours and re-analyzed to assess the formulation stability. The analysis results indicated formulations were stable at room temperature at least 3 hours.
Based on these results, all formulations were accurately prepared and were stable for the purpose of this study.
Any other information on results incl. tables
Plasma Analysis
Plasma samples collected from the vehicle control group animals at 18 hours post dose, and from the test substance treatment group animals at 15 minutes, 30 minutes, 1, 2, 4, 8, and 18 hours post-dose were analyzed by the Sponsor using a validated LC-MS/MS method [A162.DR (LC/MS/MS Analysis of Clossonate (RD 28636, CID 38047) in Mouse Plasma]. The analysis results are indicated as follows: Plasma sample from one of the vehicle control treated animals (animal number# 41) was free of interferences. Plasma concentrations of the test substance treated animals at different time intervals are summarized in the following table:
Group/Treatment | Average TM 09-217c Concentrations (ng/mL) Post Dose | ||||||
15 min | 30 min | 1 hr | 2 hr | 4 hr | 8 hr | 18 hr | |
vehicle control | NS | NS | NS | NS | NS | NS | * |
500 mg/kg | 9 | 11 | 12 | 19 | 11 | 1 | 0 |
1000 mg/kg | 16 | 20 | 21 | 39 | 21 | 15 | 5 |
2000 mg/kg | 40 | 39 | 49 | 51 | 48 | 18 | 23 |
NS = Not sampled; * data from one animal (animal #41) free of TM 09-217c.
Toxicokinetic Evaluation
Mean plasma concentrations (bio-analytical data) of TM 09-217c were used to determine toxicokinetic parameters using Microsoft Office Professional, Excel 2010. The mean toxicokinetic parameters such as Cmax (maximum plasma concentration), Tmax (time at which Cmax was observed). AUC0-thr (the area under the concentration vs time curve), estimated total systemic clearance (CLsys) were calculated. The mean toxicokinetic parameters are presented in the following Table:
Dose (mg/kg) | Cmax (ng/mL) | Tmax (hr) | AUC(0-t) (ng/mL·hr) | CL(sys) (mL/kg/min) |
500 | 18.7 | 1.7 | 83.3 | 101197 |
1000 | 39.3 | 2.0 | 280.5 | 60389 |
2000 | 54 | 4.7 | 521.8 | 7 0666 |
Cmax (maximum plasma concentration); Tmax (time at which Cmax was observed)
AUC0-t (the area under the concentration vs time curve)
CL(sys) estimated total systemic clearance
The results indicate an apparent increase in Cmax values trended toward linearity with increases in the relative ratio of dose of 1:2.2:4 and values of 1:2.1:2.9. The systemic exposure was greater than predicted with relative ratio increases in AUC(0-18hr) of 1:3.4:6.3, which also followed the CLsys observed and the suggestion of greater clearance at the low dose relative to the mid and high dose groups.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Under the described conditions of the study, a single intraperitoneal administration of TM 09-217c at doses up to and including a dose of 2000 mg/kg did not induce a significant increase in the frequency of cells with structural or numerical aberrations in the bone marrow of male ICR mice. Therefore, TM 09-217c was concluded to be negative in the mouse chromosome aberration assay. - Executive summary:
The test substance, TM 09-217c, was evaluated for its genotoxic potential as measured by its ability to induce structural and/or numerical chromosome aberrations in mouse bone marrow of male ICR mice, according to OECD test guideline 475. with a single intraperitoneal administration of TM 09-217c at doses up to and including a dose of 2000 mg/kg did not induce a significant increase in the frequency of cells with structural or numerical aberrations in the bone marrow of male ICR mice. Therefore, TM 09-217c was concluded to be negative in the mouse chromosome aberration assay.
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