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EC number: 300-723-4 | CAS number: 127823-21-6
- 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
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- Endpoint summary
- Stability
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- 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 cell study: DNA damage and/or repair
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Experimental Start Date: 04th February 2022
Experimental Completion Date: 29th March 2022 - Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 022
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 489 (In vivo Mammalian Alkaline Comet Assay)
- Version / remarks:
- 2016
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian comet assay
Test material
- Reference substance name:
- (octahydro-4,7-methano-1H-indenyl)methyl acrylate
- EC Number:
- 300-723-4
- EC Name:
- (octahydro-4,7-methano-1H-indenyl)methyl acrylate
- Cas Number:
- 127823-21-6
- Molecular formula:
- C14H20O2
- IUPAC Name:
- {tricyclo[5.2.1.0²,⁶]decan-8-yl}methyl prop-2-enoate
- Test material form:
- liquid
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on species / strain selection:
- The rat was selected as there is a large volume of background data in this species and has been specifically requested by ECHA for this comet assay (ECHA decision number TPE-D-2114557356-42-01/F).
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: -6 male young adult out-bred Sprague Dawley rats (Crl:CD(SD)) were obtained from Charles River (UK)
Ltd., Margate, UK for use in the Range-Finder
-27 male young adult out-bred Sprague Dawley rats (HSD:Sprague DawleySD) were obtained from
Envigo, Blackthorn, UK for use in the Main Experiment
- Age at study initiation: 7 to 8 weeks old
- Weight at study initiation: ca. 250 g
- Assigned to test groups randomly: animals were randomly allocated to cages. Male rats only due to the potential analysis of gonadal cells and to ethically minimise animal testing.
- Fasting period before study: no
- Housing: Animals were housed in wire topped, solid bottomed cages, with three animals per cage. Bedding was provided on a weekly basis to each cage by use of clean European softwood bedding (Datesand Ltd.,
Manchester) and provided with wooden Aspen chew blocks and rodent retreats.
-Diet:: ad libitum access to 5LF2 EU Rodent Diet
- Water ad libitum via water bottles
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-25 °C
- Humidity (%): 40-70%
- Air changes (per hr): 15 air changes per hour
- Photoperiod: 12 hrs dark / 12 hrs light:
IN-LIFE DATES:
In-life Start Date: 07th February 2022
In-life End Date: 08th March 2022
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Corn oil
- Details on exposure:
- Formulations were freshly prepared prior to each dosing occasion for the Range-Finder (dose group 1RF) and prepared once for each dose group in the Main Experiment. (octahydro-4,7-methano-1H-indenyl) methyl acrylate was formulated in corn oil as follows:
The test article was weighed out into a pre-labelled bottle and vehicle was added to achieve the final volume. Formulations were stirred on a magnetic stirrer to homogenise and aliquoted (as required). - Duration of treatment / exposure:
- 21 hours
- Frequency of treatment:
- The test article and vehicle control were given as two administrations, at 0 and 21 hours; the positive control was administered once only at 21 hours.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day (actual dose received)
- Remarks:
- Control - vehicle only
- Dose / conc.:
- 500 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- Dose / conc.:
- 2 000 mg/kg bw/day (nominal)
- Dose / conc.:
- 200 mg/kg bw/day (nominal)
- Remarks:
- positive control
- No. of animals per sex per dose:
- 3 male animals were dosed during the Range-Finder Experiment
5 male animals were dosed during the Main Experiment, plus 3 males for the positive control
Main Experiment animals were dosed in replicate cage order i.e. cage 1 of Groups 1-4 dosed in ascending group order then cage 2 of Groups 1-4 in ascending group order. Group 5 was dosed at a time that allowed necropsy of these animals after Group 4 necropsy. Animals were not fasted prior to administration and were sampled at 24 hours. - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Positive control:
The vehicle control group consisted of animals dosed with corn oil. The vehicle was selected as it has been used in previous in vivo studies with this compound.
The positive control, Ethyl Methanesulfonate (EMS, Sigma-Aldrich Chemical Co, Poole, UK) was freshly prepared in purified water as follows:
-dose volume (ml/kg): 10
-concentration of EMS solution (mg/ml): 20
-dose of EMS administered (mg/kg): 200
Examinations
- Tissues and cell types examined:
- The liver, stomach, duodenum and gonad were removed from each control (vehicle and positive) and test article treated animal.
For histopathology, a sample of liver, stomach, duodenum and gonad from vehicle control and test article treated animals only was removed. Liver, stomach and duodenum samples were immediately preserved in neutral buffered formalin and stored at room temperature. Gonad samples were immediately preserved in modified Davidson’s fluid and stored at room temperature. No histopathology samples were preserved for the positive control animals.
Preserved liver, stomach, duodenum and gonad samples were embedded in wax blocks and sectioned at 5 µm nominal. Liver, stomach and duodenum slides were stained with haematoxylin and eosin and examined by the Study Pathologist. Gonad samples were not examined as the somatic tissues did not show genotoxic potential - Details of tissue and slide preparation:
- Preparation of Cell Suspensions
The comet liver samples were washed thoroughly in Merchants solution and placed in fresh buffer. The samples were cut into small pieces in Merchants solution and the pieces of liver were then pushed through bolting cloth (pore size of 150 µm) with approximately 4 mL of Merchants solution to produce single cell suspensions.
The comet stomach samples were washed in ice cold Merchants solution and then incubated on ice for 15 minutes prior to processing. After incubation the stomach samples were removed from the Merchants solution and the inner surface gently scraped (released material discarded) using the back of a scalpel blade. Cells were gently scraped from the inside surface of the stomach using the back of a scalpel blade in 200 µL of fresh Merchants solution to produce single cell suspensions.
The comet duodenum samples were washed thoroughly in ice cold Merchants solution; each sample was vortexed in ice cold Merchants solution for approximately 15 seconds. The tissue was removed from the Merchants solution and the inner surface gently scraped twice (released material discarded) using the back of a scalpel blade. The tissue was vortexed in ice cold Merchants solution for a further 15 seconds prior to gently scraping the inside of the duodenum three times with the back of a scalpel blade in 150 µL of fresh Merchants solution to produce single cell suspensions.
The comet gonad samples were prepared by making an incision along the length of a single gonad, removing the contents from the membrane and discarding the membrane. The remaining tissue was cut into small pieces and gently pushed through bolting cloth (pore size of 150 µm) with approximately 10 mL of Merchants solution to produce single cell suspensions.
All cell suspensions were held on ice prior to slide preparation.
Slide Preparation
Three slides, labelled ‘A’, ‘B’ and ‘C’ were prepared per single cell suspension per tissue. Slides were labelled with the study number, appropriate animal tag number and tissue. Slides were dipped in molten normal melting point agarose (NMA) such that all of the clear area of the slide and at least part of the frosted area was coated. The underside of the slides was wiped clean and the slides allowed to dry. 40 µL of each single cell suspension was added to 400 µL of 0.7% low melting point agarose (LMA) at approximately 37°C. 100 µL of cell suspension/agarose mix was placed on to each slide. The slides were then coverslipped and allowed to gel on ice
Unwinding and Electrophoresis
Following lysis, slides were washed in purified water for 5 minutes, transferred to electrophoresis buffer (300 mM NaOH, 1 mM EDTA, pH>13) at 2-8°C and the DNA unwound for 20 minutes (stomach and duodenum) or 30 minutes (liver and gonad). At the end of the unwinding period the slides were electrophoresed in the same buffer at 0.7 V/cm for 20 minutes (stomach and duodenum) or 40 minutes (liver and gonad). As not all slides could be processed at the same time a block design was employed for the unwinding and electrophoretic steps in order to avoid excessive variation across the groups for each electrophoretic run; i.e. for all animals the same number of triplicate slides was processed at a time.
Neutralisation
At the end of the electrophoresis period, slides were neutralised in 0.4 M Tris, pH 7.0 (3 x 5 minute washes). After neutralisation the slides were dried and stored at room temperature prior to scoring.
Staining
Prior to scoring, the slides were stained with 100 µL of 2 µg/mL ethidium bromide and coverslipped. - Evaluation criteria:
- For valid data, the test article was considered to induce DNA damage if:
1. A least one of the test doses exhibited a statistically significant increase in tail intensity, in any tissue, compared with the concurrent vehicle control
2. The increase was dose related in any tissue.
3. The increase exceeded the laboratory’s historical control data for that tissue.
The test article was considered positive in this assay if all of the above criteria were met.
The test article was considered negative in this assay if neither of the above criteria were met and target tissue exposure was confirmed.
Results which only partially satisfied the criteria were dealt with on a case-by-case basis. Biological relevance was taken into account, for example comparison of the response against the historical control data, consistency of response within and between dose levels and any confirmatory experiments - Statistics:
- Treatment of Data
After completion of microscopic analysis and decoding of the data the percentage tail intensity (i.e. %DNA in the tail) was calculated.
Data were treated as follows:
1. The median value per slide was calculated
2. The mean of the slide medians was calculated to give the mean animal value
3. The mean of the animal means and standard error of the mean was calculated for each group.
Tail intensity data for each slide were supplied for statistical analysis. The median of the log-transformed tail intensities from each slide was averaged to give an animal summary statistic. Where the median value on a slide was zero, a small constant (0.0001) was added before taking the logarithm and calculating the average for the animal. This animal average was used in the statistical analysis.
Data was analysed using one-way analysis of variance (ANOVA) with the fixed factor for treatment group. The positive control group was excluded from this analysis. Levene’s test was used to test for equality of variances among groups. This showed no evidence of heterogeneity (P>0.01). Comparisons between each treated group and control were made using Dunnett’s test. The test was one-sided looking for an increase in response with increasing dose. The back-transformed difference and p value are reported. In addition, a linear contrast was used to test for an increasing dose response.
The positive control group was compared to the control group using a two-sample t test. Levene’s test was used to test for equality of variances between the groups. This showed no evidence of heterogeneity (P>0.01). The test was one-sided looking for an increase in response with increasing dose. The back-transformed difference and p-value are reported.
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- RANGE-FINDER RESULTS
(octahydro-4,7-methano-1H-indenyl) methyl acrylate at 2000 mg/kg/day. No clinical observations of toxicity were observed for any animal on Day 1. Decreased activity was noted for 2 out of 3 animals on Day 2, 2 hours post dose. No further clinical signs were observed for the remainder of the Range-Finder Experiment. There were only small changes in animal body weight between Day 1 and 2, with the group mean body weight percentage change value of +0.4%.
From these results, the current maximum recommended dose of 2000 mg/kg/day was tolerated and selected as the maximum dose for the Main Experiment. Two lower doses of 500 and 1000 mg/kg/day (equivalent to 25% and 50% of the maximum dose) were also selected.
Post dose observations and body weights are presented in below tables Individual Post Dose Observations and Individual and Group Mean Body Weights, respectively.
MAIN EXPERIMENT RESULTS
Formulations Analysis
Analyses demonstrated that the test article formulations at 50, 100 and 200 mg/mL were homogeneous (0.39-4.12% relative standard deviation (RSD), which fell within target criteria of =5%) and met criteria (100±15% of the nominal test article concentrations) for acceptable achieved concentration (mean values of 102-106%). The formulations were therefore considered acceptable. No test article was detected in the vehicle sample.
Post Dose Observations
There were no clinical observations of toxicity for any animal dosed with the vehicle, (octahydro-4,7-methano-1H-indenyl) methyl acrylate (at 500, 1000 or 2000 mg/kg/day) or the positive control (EMS). Please see table: Individual Post Dose Observations.
Body Weights
There was no clear test article related impact on animal body weights between Day 1 and Day 2 with group mean body weight change values of +2.5%, +2.9% and +3.6% for 500, 1000 and 2000 mg/kg/day, respectively, compared to +3.6% for the concurrent vehicle control group. Please see below tables: Individual and Group Mean Body Weights and Summary of Body Weight Percentage Change.
Bioanalysis
Plasma was processed from whole blood samples as a contingency for systemic exposure confirmation. Analysis of these samples was not performed
Clinical Pathology
Clinical Chemistry
Increased cholesterol was recorded for animals from all groups administered (octahydro-4,7-methano-1H-indenyl) methyl acrylate.
Increased urea was noted for animals administered 1000 or 2000 mg/kg/day (octahydro-4,7-methano-1H-indenyl) methyl acrylate and increased creatinine for animals administered 500, 1000, or 2000 mg/kg/day (octahydro-4,7-methano-1H-indenyl) methyl acrylate.
While the clinical chemistry changes were generally very small, based on the acute nature of this study (24 hours) at the maximum-tolerated dose, and because the values in (octahydro-4,7-methano-1H-indenyl) methyl acrylate-treated animals were outside the control range and often noted with a dose relationship, findings described were considered related to (octahydro-4,7-methano-1H-indenyl) methyl acrylate.
Other differences in individual clinical pathology parameters were observed for animals administered the test article; however, they were considered not test article related due to the negligible magnitude of the change, individual animal variability, and overlap of values for test article treated animals with concurrent control values. Please find below results table: Individual and Group Mean Clinical Chemistry.
Histopathology
On macroscopic examination, no changes were considered related to (octahydro-4,7-methano-1H-indenyl) methyl acrylate. Tissues were considered macroscopically unremarkable or the findings observed were generally consistent with the usual pattern of findings in rats of this strain and age.
On microscopic examination, changes related to (octahydro-4,7-methano-1H-indenyl) methyl acrylate were recorded for the liver. Decreased hepatocyte glycogen was recorded with a dose relationship for animals administered 1000 or 2000 mg/kg/day.
Glycogen is normally stored in the hepatocytes in large, often perinuclear vacuoles with a granular or feathery appearance. Decreased glycogen vacuolation was noted in animals administered (octahydro-4,7-methano-1H-indenyl) methyl acrylate. Animals were not fasted prior to necropsy and were also sacrificed in replicate order (within 1 hour of each other); as such, this decrease in glycogen was attributed directly or indirectly to the effects of (octahydro-4,7-methano-1H-indenyl) methyl acrylate. This decrease may indicate an increased utilization of glycogen, possibly due to the increased metabolism in the liver or decreased food consumption.
Comet Analysis
Comet data for liver are presented in tables: Liver: Animal Comet Data (animal values) and Liver: Individual Slide Data (slide values), and summarised as group means in Table (octahydro-4,7-methano-1H-indenyl) methyl acrylate: Summary of Group Mean Data – Liver. Comet data for stomach are presented in Table Stomach: Animal Comet Data(animal values), Table Stomach: Individual Slide Data (slide values), and summarised as group means in Table (octahydro-4,7-methano-1H-indenyl) methyl acrylate: Summary of Group Mean Data – Stomach. Comet data for duodenum are presented in Table Duodenum: Animal Comet Data (animal values), Table Duodenum: Individual Slide Data (slide values), and summarised as group means in Table (octahydro-4,7-methano-1H-indenyl) methyl acrylate: Summary of Group Mean Data – Duodenum.
Any other information on results incl. tables
- The vehicle control data were comparable to laboratory historical control data for each tissue
- The positive control induced responses that were compatible with the laboratory historical control data and produces are statistically significant compared to the concurrent vehicle control
- Adequate numbers of cells and doses were analysed
- The high dose was considered to be the maximum recommended dose.
As dosing was via oral gavage, exposure to the stomach and duodenum was assured. With regards to the liver, decreased hepatocyte glycogen indicated liver perturbations following dosing, which was attributed directly or indirectly to the effects of the test article. Furthermore, while the clinical chemistry changes were small, they were determined to be test article-related providing indirect evidence of a systemic response. Neither the clinical chemistry nor histopathology findings were notable, but combined provide indirect evidence of systemic test article exposure and therefore liver exposure as a well perfused tissue.
The assay data were therefore considered valid.
Validity of Data
The data generated in this study confirm that:
assay data were therefore considered valid.
Data Analysis
There was no dose-related increase in %hedgehogs in liver, stomach or duodenum, thus demonstrating that treatment with (octahydro-4,7-methano-1H-indenyl) methyl acrylate did not cause excessive DNA damage that could have interfered with comet analysis.
Animals treated with (octahydro-4,7-methano-1H-indenyl) methyl acrylate at all doses exhibited group mean tail intensities that were similar to the concurrent vehicle control group and that fell within the 95% reference range of the laboratory's historical vehicle control data. There were no statistically significant increases in tail intensity for any of the groups receiving the test article, compared to the concurrent vehicle control, with no evidence of a dose response.
There were individual animal liver %tail intensity values in each test article dosed group that exceeded the upper limit of the 95% reference range (1.80%). However, there was only one animal at 500 mg/kg/day (R0105) and one animal at 2000 mg/kg/day (R0304) that exceeded the upper limit of the observed range of all vehicle control dosed animals in the laboratory’s historical vehicle control data (2.37%). Furthermore, these small increases were not reproduced in all animals in any dose group, did not contribute to statistically significant increases for any group compared to the vehicle control group, and did not occur in a dose-related manner. As such, there were considered of no biological relevance.
These data were considered clearly negative in the liver, stomach and duodenum.
(octahydro-4,7-methano-1H-indenyl) methyl acrylate: Summary of Group Mean Data – Liver
Group/Dose Level (mg/kg/day) | Tail Intensity | Mean % Hedgehogs | |||||
Mean | SEM | Back-Transformed Difference from Vehicle | Ranked | P-value | Significance | ||
|
|
|
|
|
|
|
|
1/ Vehicle (0) | 0.98 | 0.22 | - | - | - | - | 0.39 |
2/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (500) | 1.56 | 0.52 | 1.55 | U | 0.3636 | NS | 0.86 |
3/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (1000) | 1.33 | 0.28 | 1.43 | U | 0.4367 | NS | 0.68 |
4/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | 1.34 | 0.31 | 1.58 | U | 0.3481 | NS | 0.68 |
5/ EMS (200) | 21.71 | 1.46 | 32.22 | U | 0.0001 | *** | 0.89 |
Dose response: (groups 1,2,3,4 ) |
|
|
| U | 0.2026 | NS | N/A |
(octahydro-4,7-methano-1H-indenyl) methyl acrylate: Summary of Group Mean Data – Stomach
Group/Dose Level (mg/kg/day) | Tail Intensity | Mean % Hedgehogs | |||||
Mean | SEM | Back-Transformed Difference from Vehicle | Ranked | P-value | Significance | ||
|
|
|
|
|
|
|
|
1/ Vehicle (0) | 1.09 | 0.26 | - | - | - | - | 9.08 |
2/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (500) | 0.75 | 0.19 | 0.63 | U | 0.9793 | NS | 12.32 |
3/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (1000) | 0.56 | 0.12 | 0.53 | U | 0.9932 | NS | 8.01 |
4/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | 0.76 | 0.17 | 0.72 | U | 0.9530 | NS | 9.18 |
5/ EMS (200) | 9.79 | 2.04 | 11.07 | U | 0.0004 | *** | 11.24 |
Dose response: (groups 1,2,3,4 ) |
|
|
| U | 0.8329 | NS | N/A |
EMS | Ethyl Methanesulfonate |
SEM | Standard Error of Mean |
N/A | Not applicable |
NS | Not significant (P>0.05) |
*** | P≤0.001 |
U | Unranked |
(octahydro-4,7-methano-1H-indenyl) methyl acrylate: Summary of Group Mean Data – Duodenum
Group/Dose Level (mg/kg/day) | Tail Intensity | Mean % Hedgehogs | |||||
Mean | SEM | Back-Transformed Difference from Vehicle | Ranked | P-value | Significance | ||
|
|
|
|
|
|
|
|
1/ Vehicle (0) | 0.45 | 0.11 | - | - | - | - | 10.35 |
2/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (500) | 0.85 | 0.22 | 1.89 | U | 0.2150 | NS | 8.78 |
3/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (1000) | 0.72 | 0.20 | 1.70 | U | 0.2884 | NS | 10.34 |
4/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | 0.64 | 0.28 | 1.28 | U | 0.5338 | NS | 9.92 |
5/ EMS (200) | 6.93 | 1.76 | 20.60 | U | 0.0001 | *** | 7.81 |
Dose response: (groups 1,2,3,4 ) |
|
|
| U | 0.3369 | NS | N/A |
EMS | Ethyl Methanesulfonate |
SEM | Standard Error of Mean |
N/A | Not applicable |
NS | Not significant (P>0.05) |
*** | P≤0.001 |
U | Unranked |
RANGE-FINDER TABLES
Individual Post Dose Observations
Group / | Animal ID and Sex | Clinical Sign | |||||||||||
Day 1 (hours after administration) | Day 2 (hours after administration) | ||||||||||||
Prior to dose | Imm | 0.5 | 1 | 2 | 4-6 | Prior to dose | Imm | 0.5 | 1 | 2 | 4-6 | ||
1RF / (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | R5001M | ü | ü | ü | ü | ü | ü | ü | ü | ü | ü | DA | ü |
R5002M | ü | ü | ü | ü | ü | ü | ü | ü | ü | ü | ü | ü | |
R5003M | ü | ü | ü | ü | ü | ü | ü | ü | ü | ü | DA | ü |
Key to Range-Finder Clinical Observations | |
ü | No remarkable observations |
DA | Reduced activity |
Individual and Group Mean Body Weights
Group / Sex | Treatment | Animal Number | Day 1 | Day 2 | Group Mean Weight Change (Day 1-2) (%) |
1RF / M | (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | R5001 | 248 | 247 |
|
| R5002 | 254 | 255 |
| |
| R5003 | 242 | 246 |
| |
Group mean (g) | 248 | 249 | +0.4 |
MAIN EXPERIMENT TABLES
Individual Post Dose Observations
Individual Physical Examinations
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS | |||||||||||
Group 1 2 3 4 5 | |||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 200 | |||||||||||
session | |||||||||||
Group/Sex | Animal Number |
| Observation | Phase | Day (s) | 3
| 4
| 6 | 8 | 10 | 12 |
1/M | R0001 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
1/M | R0002 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
1/M | R0003 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
1/M | R0004 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
1/M | R0005 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
1/M | R0006 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
p = present
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS | |||||||||||
Group 1 2 3 4 5 | |||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 200 | |||||||||||
session | |||||||||||
Group/Sex | Animal Number |
| Observation | Phase | Day (s) | 3
| 4
| 6 | 8 | 10 | 12 |
2/M | R0001 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
2/M | R0002 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
2/M | R0003 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
2/M | R0004 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
2/M | R0005 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
2/M | R0006 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
p = present
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS | |||||||||||
Group 1 2 3 4 5 | |||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 200 | |||||||||||
session | |||||||||||
Group/Sex | Animal Number |
| Observation | Phase | Day (s) | 3
| 4
| 6 | 8 | 10 | 12 |
3/M | R0001 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
3/M | R0002 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
3/M | R0003 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
3/M | R0004 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
3/M | R0005 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
3/M | R0006 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
p = present
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS | |||||||||||
Group 1 2 3 4 5 | |||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 200 | |||||||||||
session | |||||||||||
Group/Sex | Animal Number |
| Observation | Phase | Day (s) | 3
| 4
| 6 | 8 | 10 | 12 |
4/M | R0001 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
4/M | R0002 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
4/M | R0003 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
4/M | R0004 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
4/M | R0005 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
4/M | R0006 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
p = present
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS | |||||||||||
Group 1 2 3 4 5 | |||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 200 | |||||||||||
session | |||||||||||
Group/Sex | Animal Number |
| Observation | Phase | Day (s) | 3
| 4
| 6 | 8 | 10 | 12 |
5/M | R0001 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
5/M | R0002 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
5/M | R0003 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
5/M | R0004 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
5/M | R0005 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
5/M | R0006 | Normal | No remarkable observations | DSNG | 1/2 | p/p | p/p | p/- | p/- | p/- | -/p |
p = present
Session |
|
3 | Prior to dose |
4 | Immediate |
6 | 1 hour post dose |
8 | 2 hours post dose |
10 | 4 hours post dose |
12 | Prior to necropsy |
Individual and Group Mean Body Weights
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS | ||||||
Group 1 2 3 4 | ||||||
Dose level (mg/kg/day) 0 500 1000 2000 | ||||||
Data presented in g | ||||||
Group/Sex | Animal Number | Phase Day PRED 1 DSNG1 DSNG2 |
| |||
1/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 227.4 207.6 200.5 200.6 205.4 211.6
208.9 10.03 6
| 229.1 211.4 204.2 205.8 208.3 214.1
212.2 9.06 6 | 233.8 221.2 216.3 215.1 210.1 222.3
219.8 8.16 6 | |
2/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 204.8 204.3 212.1 206.1 206.2 204.0
206.3 3.01 6 | 207.2 205.8 216.2 209.2 209.4 210.2
209.7 3.59 6 | 212.7 210.3 224.3 212.4 216.0 213.4
214.9 4.98 6 | |
3/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N 03 |
| 204.8 196.2 196.1 201.1 212.8 216.1
204.5 8.42 6 | 212.4 202.7 203.0 206.4 213.6 223.7
210.5 8.08 6 | 220.4 208.1 208.9 210.2 218.1 233.7
216.6 9.81 6 | |
4/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 200.8 199.8 193.4 207.4 192.0 207.8
200.2 6.69 6 | 200.6 197.0 197.7 208.8 194.1 208.3
201.1 6.14 6 | 204.7 208.4 204.2 223.4 199.2 209.6
208.3 8.27 6 | |
5/M | R0001 R0002 R0003
Mean SD N |
| 209.2 206.1 208.4
207.9 1.61 3 | 212.1 206.8 210.6
209.8 2.73 3 | 221.1 213.7 222.6
219.1 4.76 3 |
|
Summary of Body Weight Percentage Change
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS | ||||||
Group 1 2 3 4 | ||||||
Dose level (mg/kg/day) 0 500 1000 2000 | ||||||
Data presented in "%" Interval X through X | ||||||
Group/Sex | Animal Number | Phase Day DSNG 1 - 2 |
| |||
1/M | Mean SD N |
| 3.6 1.86 6 |
|
| |
2/M | Mean SD N |
| 2.5 0.89 6 |
|
| |
3/M | Mean SD N |
| 2.9 0.94 6 |
|
| |
4/M | Mean SD N |
| 3.6 2.39 6 |
|
| |
5/M | Mean SD N |
| 4.4 1.19 3 |
|
|
Individual and Group Mean Clinical Chemistry
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS |
| ||||||||||||
Group 1 2 3 4 |
| ||||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 |
| ||||||||||||
ASTP IU/L phase Dosing | ALTP IU/L Dosing | HALP IU/L Dosing | CHOL mmol/L Dosing | T.BI umol/L Dosing | TP g/L Dosing |
|
| ||||||
Group/Sex | Animal Number | Day | 2 | 2 | 2 | 2 | 2 | 2 |
|
|
| ||
1/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 111 125 110 119 119 103
115 7.9 6 | 67 80 59 70 68 62
68 7.3 6 | 240 361 325 270 262 367
304 54.2 6 | 2.4 2.2 2.4 2.3 2.4 2.3
2.3 0.10 6
| <1.7* <1.7* <1.7* <1.7* <1.7* <1.7*
<1.7 0.00 6 | 52 52 51 53 55 52
53 1.4 6 |
|
|
| ||
2/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 119 115 114 101 107 103
110 7.2 2 | 74 89 74 65 68 59
72 10.3 6 | 403 390 342 344 363 287
355 41.2 6 | 2.7 2.4 2.5 2.3 2.8 2.5
2.5 0.19 6 | <1.7* <1.7* <1.7* <1.7* <1.7* <1.7*
<1.7 0.00 6 | 56 54 54 55 52 54
54 1.3 6 |
|
|
|
*= Value shown used in descriptive statistics
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS |
| ||||||||||||
Group 1 2 3 4 |
| ||||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 |
| ||||||||||||
ASTP IU/L phase Dosing | ALTP IU/L Dosing | HALP IU/L Dosing | CHOL mmol/L Dosing | T.BI umol/L Dosing | TP g/L Dosing |
|
| ||||||
Group/Sex | Animal Number | Day | 2 | 2 | 2 | 2 | 2 | 2 |
|
|
| ||
3/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 109 131 121 107 104 103
113 11.1 6 | 69 86 58 74 82 79
75 10.1 6 | 279 269 291 284 309 351
297 29.6 6 | 2.7 2.5 2.5 2.7 2.5 2.5
2.6 0.10 6
| <1.7* <1.7* <1.7* <1.7* <1.7* <1.7*
<1.7 0.00 6 | 53 58 55 55 57 53
55 2.0 6 |
|
|
| ||
4/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 88 112 108 89 89 96
97 10.5 2 | 79 88 106 81 59 57
78 18.4 6 | 240 293 317 299 250 207
268 42.0 6 | 2.9 2.7 2.5 2.7 2.9 2.6
2.7 0.16 6 | <1.7* <1.7* <1.7* <1.7* <1.7* <1.7*
<1.7 0.00 6 | 55 59 54 54 56 55
56 1.9 6 |
|
|
|
*= Value shown used in descriptive statistic
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS |
| ||||||||||||
Group 1 2 3 4 |
| ||||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 |
| ||||||||||||
ALB g/L phase Dosing | GLOB g/L Dosing | A/G Ratio Dosing | NA mmol/L Dosing | K mmol/L Dosing | CL mmol/L Dosing |
|
| ||||||
Group/Sex | Animal Number | Day | 2 | 2 | 2 | 2 | 2 | 2 |
|
|
| ||
1/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 40 41 37 40 41 40
40 1.5 6 | 12 11 14 13 14 12
13 1.2 6 | 3.3 3.7 2.6 3.1 2.9 3.3
3.2 0.38 6 | 140 141 136 141 140 140
140 1.9 6 | 5.3 5.0 5.0 4.9 4.8 5.0
5.0 0.17 6 | 100 100 99 101 100 99
100 0.8 6 |
|
|
| ||
2/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 41 40 41 43 40 41
41 1.1 6 | 15 14 13 12 12 13
13 1.2 6 | 2.7 2.9 3.2 3.6 3.3 3.2
3.2 0.31 6 | 139 141 138 141 140 141
140 1.3 6 | 5.3 4.8 5.0 4.9 5.2 4.9
5.0 0.19 6 | 99 100 99 101 100 101
100 0.9 6 |
|
|
|
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS |
| ||||||||||||
Group 1 2 3 4 |
| ||||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 |
| ||||||||||||
ALB g/L phase Dosing | GLOB g/L Dosing | A/G Ratio Dosing | NA mmol/L Dosing | K mmol/L Dosing | CL mmol/L Dosing |
|
| ||||||
Group/Sex | Animal Number | Day | 2 | 2 | 2 | 2 | 2 | 2 |
|
|
| ||
3/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 40 44 40 42 43 40
42 1.8 6 | 13 14 15 13 14 13
14 0.8 6 | 3.1 3.1 2.7 3.2 3.1 3.1
3.1 0.18 6 | 140 140 139 139 140 140
140 0.5 6 | 5.0 5.1 4.8 5.4 5.1 5.1
5.1 0.19 6 | 99 99 100 99 101 100
100 0.8 6 |
|
|
| ||
4/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 42 45 42 40 42 42
42 1.6 6 | 13 14 12 14 14 13
13 0.8 6 | 3.2 3.2 3.5 2.9 3.0 3.2
3.2 0.21 6 | 141 142 141 141 139 140
141 1.0 6 | 5.2 5.1 4.8 4.8 5.3 4.9
5.0 0.21 6 | 102 101 101 101 100 100
101 0.8 6 |
|
|
|
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS |
| ||||||||||||
Group 1 2 3 4 |
| ||||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 |
| ||||||||||||
CAL mmol/L phase Dosing | P mmol/L Dosing | HCRE umol/L Dosing | UREA mmol/L Dosing | GLUC mmol/L Dosing |
|
|
| ||||||
Group/Sex | Animal Number | Day | 2 | 2 | 2 | 2 | 2 |
|
|
|
| ||
1/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 2.59 2.64 2.57 2.65 2.61 2.62
2.61 0.030 6 | 2.8 3.0 2.7 2.7 2.5 2.6
2.7 0.17 6 | 12 16 17 15 14 14
15 1.8 6 | 3.4 3.6 4.0 3.7 3.3 4.1
3.7 0.32 6 | 11.5 9.2 11.0 11.9 11.7 13.5
11.5 1.40 6 |
|
|
|
| ||
2/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 2.67 2.64 2.67 2.57 2.67 2.61
2.64 0.041 6 | 3.0 2.8 3.1 2.8 3.0 3.1
3.0 0.14 6 | 21 19 18 18 18 20
19 1.3 6 | 4.1 4.6 3.9 3.0 3.6 3.3
3.8 0.58 6 | 8.6 9.2 10.7 9.3 10.3 10.1
9.7 0.79 6 |
|
|
|
|
Test Article vehicle (octahydro-4,7-methano-1H-indenyl) methyl acrylate EMS |
| ||||||||||||
Group 1 2 3 4 |
| ||||||||||||
Dose level (mg/kg/day) 0 500 1000 2000 |
| ||||||||||||
CAL mmol/L phase Dosing | P mmol/L Dosing | HCRE umol/L Dosing | UREA mmol/L Dosing | GLUC mmol/L Dosing |
|
|
| ||||||
Group/Sex | Animal Number | Day | 2 | 2 | 2 | 2 | 2 |
|
|
|
| ||
3/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 2.60 2.71 2.60 2.63 2.50 2.64
2.61 0.069 6 | 2.8 2.9 2.7 2.9 2.8 3.3
2.9 0.21 6 | 19 19 18 18 19 18
19 0.5 6 | 4.0 4.4 4.8 4.2 3.9 3.5
4.1 0.45 6 | 10.6 11.2 12.2 11.5 11.6 12.0
11.5 0.57 6 |
|
|
|
| ||
4/M | R0001 R0002 R0003 R0004 R0005 R0006
Mean SD N |
| 2.60 2.64 2.46 2.68 2.63 2.53
2.59 0.081 6 | 2.8 3.0 3.2 2.7 3.0 2.8
2.9 0.18 6 | 19 22 15 17 18 17
18 2.4 6 | 4.4 6.3 2.7 4.5 3.2 4.0
4.2 1.25 6 | 10.4 9.2 10.9 10.5 11.7 10.8
10.6 0.82 6 |
|
|
|
|
Clinical Chemistry | |||||||
Code | Parameter | ||||||
ASTP | Aspartate aminotransferase | NA/K/CL | Sodium /potassium /chloride | ALB | Albumin | GLUC | Glucose |
ALTP | Alanine aminotransferase | CAL | Calcium | GLOB | Globulin | UREA | Urea |
HALP | Alkaline phosphatase | P | Inorganic phosphorous | A/G RATIO | Albumin/globulin ratio | HCRE | Creatinine |
T.BI | Bilirubin | TP | Total protein | CHOL | Total cholesterol |
|
|
Liver: Animal Comet Data
Group/ Dose Level | Animal | Slide | Total | Median Tail | Hedgehogs |
(mg/kg/day) | Number | Number | Comets | Intensity | (%) |
|
|
|
|
|
|
1/ Vehicle (0) | R0001 | L-19A | 50 | 0.64 | 0.00 |
| R0001 | L-19B | 50 | 0.60 | 1.79 |
| R0001 | L-19C | 50 | 1.29 | 1.85 |
| R0002 | L-74A | 50 | 0.36 | 1.67 |
| R0002 | L-74B | 50 | 0.20 | 0.00 |
| R0002 | L-74C | 50 | 2.55 | 0.00 |
| R0003 | L-102A | 50 | 0.15 | 0.00 |
| R0003 | L-102B | 50 | 0.14 | 0.00 |
| R0003 | L-102C | 50 | 0.14 | 0.00 |
| R0004 | L-16A | 50 | 0.37 | 0.00 |
| R0004 | L-16B | 50 | 1.41 | 0.00 |
| R0004 | L-16C | 50 | 0.43 | 0.00 |
| R0005 | L-29A | 50 | 0.89 | 0.00 |
| R0005 | L-29B | 50 | 1.72 | 0.00 |
| R0005 | L-29C | 50 | 1.53 | 0.00 |
| R0006 | L-27A | 50 | 2.06 | 1.64 |
| R0006 | L-27B | 50 | 1.04 | 0.00 |
| R0006 | L-27C | 50 | 2.06 | 0.00 |
2/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (500) | R0101 | L-59A | 50 | 0.28 | 0.00 |
R0101 | L-59B | 50 | 0.21 | 1.72 | |
R0101 | L-59C | 50 | 0.80 | 0.00 | |
| R0102 | L-10A | 50 | 0.56 | 0.00 |
| R0102 | L-10B | 50 | 0.19 | 1.89 |
| R0102 | L-10C | 50 | 0.18 | 1.89 |
| R0103 | L-8A | 95 | 0.94 | 1.92 |
| R0103 | L-8B | NE-A, NE-PS | NE-A, NE-PS | NE-A, NE-PS |
| R0103 | L-8C | 55 | 0.76 | 3.28 |
| R0104 | L-82A | 50 | 2.46 | 0.00 |
| R0104 | L-82B | 50 | 1.29 | 0.00 |
| R0104 | L-82C | 50 | 1.81 | 0.00 |
| R0105 | L-62A | 50 | 3.29 | 0.00 |
| R0105 | L-62B | 50 | 4.02 | 0.00 |
| R0105 | L-62C | 50 | 3.59 | 0.00 |
| R0106 | L-65A | 50 | 2.16 | 0.00 |
| R0106 | L-65B | 50 | 2.28 | 1.75 |
| R0106 | L-65C | 50 | 2.42 | 1.47 |
Group/ Dose Level | Animal | Slide | Total | Median Tail | Hedgehogs |
(mg/kg/day) | Number | Number | Comets | Intensity | (%) |
3/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (1000) | R0201 | L-93A | 50 | 1.48 | 1.79 |
R0201 | L-93B | 50 | 1.04 | 1.89 | |
R0201 | L-93C | 50 | 1.49 | 1.64 | |
| R0202 | L-56A | 50 | 0.66 | 0.00 |
| R0202 | L-56B | 50 | 0.29 | 1.64 |
| R0202 | L-56C | 50 | 0.22 | 0.00 |
| R0203 | L-17A | 50 | 2.03 | 3.39 |
| R0203 | L-17B | 50 | 0.73 | 0.00 |
| R0203 | L-17C | 50 | 3.27 | 0.00 |
| R0204 | L-43A | 50 | 2.23 | 0.00 |
| R0204 | L-43B | 50 | 1.55 | 0.00 |
| R0204 | L-43C | 50 | 1.75 | 0.00 |
| R0205 | L-68A | 50 | 0.11 | 0.00 |
| R0205 | L-68B | 50 | 2.40 | 1.89 |
| R0205 | L-68C | 50 | 2.85 | 0.00 |
| R0206 | L-57A | 50 | 0.36 | 0.00 |
| R0206 | L-57B | 50 | 0.58 | 0.00 |
| R0206 | L-57C | 50 | 0.85 | 0.00 |
4/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | R0301 | L-50A | 50 | 0.56 | 0.00 |
R0301 | L-50B | 50 | 1.69 | 0.00 | |
R0301 | L-50C | 50 | 1.65 | 1.69 | |
| R0302 | L-86A | 50 | 1.42 | 1.72 |
| R0302 | L-86B | 50 | 0.78 | 1.69 |
| R0302 | L-86C | 50 | 0.79 | 0.00 |
| R0303 | L-72A | 50 | 0.50 | 0.00 |
| R0303 | L-72B | 50 | 0.11 | 0.00 |
| R0303 | L-72C | 50 | 0.47 | 1.64 |
| R0304 | L-41A | 50 | 2.54 | 0.00 |
| R0304 | L-41B | 50 | 1.96 | 0.00 |
| R0304 | L-41C | 50 | 3.43 | 0.00 |
| R0305 | L-9A | 50 | 1.39 | 0.00 |
| R0305 | L-9B | 50 | 0.82 | 1.96 |
| R0305 | L-9C | 50 | 1.41 | 0.00 |
| R0306 | L-53A | 50 | 1.09 | 1.72 |
| R0306 | L-53B | 50 | 0.80 | 1.79 |
| R0306 | L-53C | 50 | 2.74 | 0.00 |
5/ EMS (200) | R0401 | L-97A | 50 | 23.54 | 1.75 |
| R0401 | L-97B | 50 | 23.27 | 0.00 |
| R0401 | L-97C | 50 | 23.44 | 0.00 |
| R0402 | L-90A | 50 | 22.28 | 0.00 |
| R0402 | L-90B | 50 | 20.26 | 1.59 |
| R0402 | L-90C | 50 | 26.22 | 3.23 |
| R0403 | L-32A | 50 | 17.29 | 0.00 |
| R0403 | L-32B | 50 | 14.57 | 0.00 |
| R0403 | L-32C | 50 | 24.53 | 1.56 |
|
|
|
|
|
NE-A | Not evaluated due to agarose detachment from slide |
NE-PS | Not evaluated due to partial gel detachment |
EMS | Ethyl Methanesulfonate |
Stomach: Animal Comet Data
Group/ Dose Level | Animal | Total | Tail Intensity (%) | Hedgehogs | |
(mg/kg/day) | Number | Comets | Mean | SD | (%) |
|
|
|
|
|
|
1/ Vehicle (0) | R0001 | 150 | 0.68 | 0.44 | 8.33 |
| R0002 | 150 | 2.09 | 0.63 | 9.73 |
| R0003 | 150 | 1.43 | 0.73 | 10.83 |
| R0004 | 150 | 1.28 | 0.56 | 7.87 |
| R0005 | 150 | 0.35 | 0.20 | 6.83 |
| R0006 | 150 | 0.69 | 0.37 | 10.54 |
2/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (500) | R0101 | 150 | 0.44 | 0.12 | 8.44 |
R0102 | 150 | 1.01 | 0.50 | 11.55 | |
R0103 | 150 | 0.68 | 0.50 | 7.61 | |
| R0104 | 150 | 0.19 | 0.19 | 11.31 |
| R0105 | 150 | 0.66 | 0.28 | 18.15 |
| R0106 | 150 | 1.51 | 0.80 | 15.53 |
3/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (1000) | R0201 | 150 | 0.55 | 0.47 | 3.69 |
R0202 | 150 | 0.60 | 0.35 | 5.34 | |
R0203 | 150 | 0.99 | 0.31 | 9.51 | |
| R0204 | 150 | 0.41 | 0.27 | 10.46 |
| R0205 | 150 | 0.27 | 0.12 | 10.49 |
| R0206 | NE-NC | NE-NC | NE-NC | NE-NC |
4/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | R0301 | 150 | 0.71 | 0.14 | 10.73 |
R0302 | 150 | 1.41 | 0.66 | 10.10 | |
R0303 | 150 | 1.07 | 0.73 | 10.07 | |
| R0304 | 150 | 0.58 | 0.24 | 7.61 |
| R0305 | 150 | 0.34 | 0.12 | 10.20 |
| R0306 | 150 | 0.43 | 0.19 | 6.90 |
5/ EMS (200) | R0401 | 150 | 7.92 | 0.40 | 8.98 |
| R0402 | 150 | 13.87 | 2.96 | 13.40 |
| R0403 | 150 | 7.58 | 0.96 | 12.19 |
|
|
|
|
|
|
SD | Standard Deviation |
EMS | Ethyl Methanesulfonate |
NE-NC | Not evaluated due to no cells |
Upon slide analysis, it was noted that there were no cells on any slide prepared for animal R0206. As there were at least 5 animals analysed for the intermediate dose group, the requirements of OECD test guideline have been met (OECD, 2016). In addition, the data are clearly negative, therefore there is no impact on data interpretation or study conclusion
Stomach: Individual Slide Data
Group/ Dose Level | Animal | Slide | Total | Median Tail | Hedgehogs |
(mg/kg/day) | Number | Number | Comets | Intensity | (%) |
|
|
|
|
|
|
1/ Vehicle (0) | R0001 | S-76A | 50 | 0.51 | 9.90 |
| R0001 | S-76B | 50 | 0.35 | 5.81 |
| R0001 | S-76C | 50 | 1.18 | 8.99 |
| R0002 | S-96A | 50 | 1.75 | 9.65 |
| R0002 | S-96B | 50 | 1.70 | 8.33 |
| R0002 | S-96C | 50 | 2.81 | 11.21 |
| R0003 | S-28A | 50 | 2.21 | 7.22 |
| R0003 | S-28B | 50 | 0.77 | 10.28 |
| R0003 | S-28C | 50 | 1.31 | 14.55 |
| R0004 | S-25A | 50 | 0.97 | 6.52 |
| R0004 | S-25B | 50 | 0.95 | 9.09 |
| R0004 | S-25C | 50 | 1.93 | 8.05 |
| R0005 | S-12A | 50 | 0.55 | 9.00 |
| R0005 | S-12B | 50 | 0.34 | 5.32 |
| R0005 | S-12C | 50 | 0.15 | 6.06 |
| R0006 | S-66A | 50 | 1.09 | 8.33 |
| R0006 | S-66B | 50 | 0.35 | 12.50 |
| R0006 | S-66C | 50 | 0.64 | 10.00 |
2/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (500) | R0101 | S-107A | 50 | 0.41 | 9.18 |
R0101 | S-107B | 50 | 0.34 | 8.65 | |
R0101 | S-107C | 50 | 0.57 | 7.55 | |
| R0102 | S-45A | 50 | 0.56 | 10.53 |
| R0102 | S-45B | 50 | 0.92 | 12.84 |
| R0102 | S-45C | 50 | 1.55 | 11.11 |
| R0103 | S-46A | 50 | 0.55 | 9.00 |
| R0103 | S-46B | 50 | 0.25 | 5.56 |
| R0103 | S-46C | 50 | 1.23 | 8.14 |
| R0104 | S-58A | 50 | 0.41 | 10.29 |
| R0104 | S-58B | 50 | 0.04 | 12.66 |
| R0104 | S-58C | 50 | 0.13 | 10.81 |
| R0105 | S-63A | 50 | 0.59 | 19.51 |
| R0105 | S-63B | 50 | 0.42 | 17.27 |
| R0105 | S-63C | 50 | 0.97 | 17.48 |
| R0106 | S-38A | 50 | 2.28 | 16.00 |
| R0106 | S-38B | 50 | 0.69 | 11.65 |
| R0106 | S-38C | 50 | 1.56 | 18.87 |
Group/ Dose Level | Animal | Slide | Total | Median Tail | Hedgehogs |
(mg/kg/day) | Number | Number | Comets | Intensity | (%) |
3/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (1000) | R0201 | S-20A | 50 | 1.09 | 3.23 |
R0201 | S-20B | 50 | 0.23 | 2.82 | |
R0201 | S-20C | 50 | 0.32 | 4.76 | |
| R0202 | S-21A | 50 | 0.82 | 6.25 |
| R0202 | S-21B | 50 | 0.20 | 4.49 |
| R0202 | S-21C | 50 | 0.78 | 5.21 |
| R0203 | S-60A | 50 | 0.66 | 7.87 |
| R0203 | S-60B | 50 | 1.26 | 10.84 |
| R0203 | S-60C | 50 | 1.06 | 9.89 |
| R0204 | S-3A | 50 | 0.45 | 11.11 |
| R0204 | S-3B | 50 | 0.13 | 12.20 |
| R0204 | S-3C | 50 | 0.65 | 7.89 |
| R0205 | S-83A | 50 | 0.39 | 11.34 |
| R0205 | S-83B | 50 | 0.27 | 8.89 |
| R0205 | S-83C | 50 | 0.14 | 11.11 |
| R0206 | S-36A | NE-NC | NE-NC | NE-NC |
| R0206 | S-36B | NE-NC | NE-NC | NE-NC |
| R0206 | S-36C | NE-NC | NE-NC | NE-NC |
4/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | R0301 | S-85A | 50 | 0.80 | 10.98 |
R0301 | S-85B | 50 | 0.77 | 11.24 | |
R0301 | S-85C | 50 | 0.54 | 10.00 | |
| R0302 | S-39A | 50 | 1.64 | 11.54 |
| R0302 | S-39B | 50 | 0.66 | 6.10 |
| R0302 | S-39C | 50 | 1.91 | 11.88 |
| R0303 | S-14A | 50 | 1.44 | 11.11 |
| R0303 | S-14B | 50 | 1.54 | 10.59 |
| R0303 | S-14C | 50 | 0.23 | 8.60 |
| R0304 | S-52A | 50 | 0.30 | 8.14 |
| R0304 | S-52B | 50 | 0.76 | 7.61 |
| R0304 | S-52C | 50 | 0.69 | 7.14 |
| R0305 | S-92A | 50 | 0.25 | 10.87 |
| R0305 | S-92B | 50 | 0.48 | 3.17 |
| R0305 | S-92C | 50 | 0.30 | 14.00 |
| R0306 | S-99A | 50 | 0.23 | 6.06 |
| R0306 | S-99B | 50 | 0.60 | 6.36 |
| R0306 | S-99C | 50 | 0.47 | 8.18 |
5/ EMS (200) | R0401 | S-103A | 50 | 7.84 | 9.70 |
| R0401 | S-103B | 50 | 8.36 | 8.49 |
| R0401 | S-103C | 50 | 7.57 | 8.51 |
| R0402 | S-101A | 50 | 16.53 | 15.49 |
| R0402 | S-101B | 50 | 10.69 | 11.59 |
| R0402 | S-101C | 50 | 14.41 | 13.04 |
| R0403 | S-26A | 50 | 8.64 | 12.50 |
| R0403 | S-26B | 50 | 7.35 | 8.57 |
| R0403 | S-26C | 50 | 6.76 | 15.53 |
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|
NE-NC | Not evaluated due to no cells |
EMS | Ethyl Methanesulfonate |
Duodenum: Animal Comet Data
Group/ Dose Level | Animal | Total | Tail Intensity (%) | Hedgehogs | |
(mg/kg/day) | Number | Comets | Mean | SD | (%) |
|
|
|
|
|
|
1/ Vehicle (0) | R0001 | 150 | 0.21 | 0.06 | 2.94 |
| R0002 | 150 | 0.83 | 0.17 | 8.54 |
| R0003 | 150 | 0.19 | 0.19 | 8.94 |
| R0004 | 150 | 0.45 | 0.34 | 6.45 |
| R0005 | 150 | 0.31 | 0.30 | 5.38 |
| R0006 | 150 | 0.70 | 0.47 | 30.23 |
2/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (500) | R0101 | 150 | 0.36 | 0.42 | 3.55 |
R0102 | 150 | 0.39 | 0.32 | 11.96 | |
R0103 | 150 | 0.87 | 0.53 | 17.11 | |
| R0104 | 150 | 1.42 | 0.63 | 2.67 |
| R0105 | 150 | 0.46 | 0.11 | 5.29 |
| R0106 | 150 | 1.58 | 0.79 | 11.35 |
3/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (1000) | R0201 | 150 | 1.15 | 0.59 | 15.61 |
R0202 | 150 | 0.30 | 0.06 | 9.39 | |
R0203 | 150 | 1.15 | 0.61 | 7.02 | |
| R0204 | 150 | 0.32 | 0.15 | 9.44 |
| R0205 | 150 | 1.18 | 0.69 | 5.53 |
| R0206 | 150 | 0.23 | 0.18 | 14.29 |
4/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | R0301 | 150 | 0.57 | 0.26 | 13.66 |
R0302 | 150 | 2.01 | 0.54 | 7.43 | |
R0303 | 150 | 0.27 | 0.11 | 6.84 | |
| R0304 | 150 | 0.35 | 0.41 | 18.69 |
| R0305 | 150 | 0.12 | 0.06 | 7.34 |
| R0306 | 150 | 0.52 | 0.03 | 5.03 |
5/ EMS (200) | R0401 | 150 | 4.61 | 1.31 | 13.33 |
| R0402 | 150 | 10.37 | 1.85 | 4.17 |
| R0403 | 150 | 5.80 | 3.30 | 5.14 |
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|
|
|
|
|
SD | Standard Deviation |
EMS | Ethyl Methanesulfonate |
Duodenum: Individual Slide Data
Group/ Dose Level | Animal | Slide | Total | Median Tail | Hedgehogs |
(mg/kg/day) | Number | Number | Comets | Intensity | (%) |
|
|
|
|
|
|
1/ Vehicle (0) | R0001 | D-87A | 50 | 0.16 | 3.06 |
| R0001 | D-87B | 50 | 0.28 | 3.33 |
| R0001 | D-87C | 50 | 0.20 | 2.38 |
| R0002 | D-54A | 50 | 0.97 | 6.45 |
| R0002 | D-54B | 50 | 0.64 | 10.61 |
| R0002 | D-54C | 50 | 0.88 | 8.45 |
| R0003 | D-61A | NE-NC | NE-NC | NE-NC |
| R0003 | D-61B | 75 | 0.05 | 10.87 |
| R0003 | D-61C | 75 | 0.32 | 6.90 |
| R0004 | D-18A | 50 | 0.24 | 6.45 |
| R0004 | D-18B | 50 | 0.26 | 5.17 |
| R0004 | D-18C | 50 | 0.83 | 7.58 |
| R0005 | D-7A | 50 | 0.64 | 3.17 |
| R0005 | D-7B | 50 | 0.27 | 7.81 |
| R0005 | D-7C | 50 | 0.03 | 5.08 |
| R0006 | D-81A | 50 | 0.89 | 23.08 |
| R0006 | D-81B | 50 | 0.16 | 32.43 |
| R0006 | D-81C | 50 | 1.05 | 34.21 |
2/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (500) | R0101 | D-64A | 50 | 0.07 | 5.36 |
R0101 | D-64B | 50 | 0.17 | 1.79 | |
R0101 | D-64C | 50 | 0.84 | 3.51 | |
| R0102 | D-77A | 50 | 0.70 | 13.11 |
| R0102 | D-77B | 50 | 0.06 | 6.56 |
| R0102 | D-77C | 50 | 0.42 | 16.13 |
| R0103 | D-24A | 50 | 1.33 | 20.63 |
| R0103 | D-24B | 50 | 0.29 | 14.52 |
| R0103 | D-24C | 50 | 0.99 | 16.13 |
| R0104 | D-98A | 50 | 1.01 | 4.84 |
| R0104 | D-98B | 50 | 1.11 | 0.00 |
| R0104 | D-98C | 50 | 2.15 | 3.13 |
| R0105 | D-89A | 50 | 0.33 | 5.45 |
| R0105 | D-89B | 50 | 0.54 | 5.00 |
| R0105 | D-89C | 50 | 0.50 | 5.45 |
| R0106 | D-2A | 50 | 2.07 | 12.70 |
| R0106 | D-2B | 50 | 0.66 | 8.47 |
| R0106 | D-2C | 50 | 2.00 | 12.70 |
Group/ Dose Level | Animal | Slide | Total | Median Tail | Hedgehogs |
(mg/kg/day) | Number | Number | Comets | Intensity | (%) |
3/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (1000) | R0201 | D-44A | 50 | 1.81 | 15.07 |
R0201 | D-44B | 50 | 0.98 | 14.71 | |
R0201 | D-44C | 50 | 0.67 | 17.19 | |
| R0202 | D-71A | 50 | 0.34 | 8.62 |
| R0202 | D-71B | 50 | 0.33 | 6.67 |
| R0202 | D-71C | 50 | 0.24 | 12.70 |
| R0203 | D-48A | 50 | 0.51 | 7.41 |
| R0203 | D-48B | 50 | 1.22 | 3.51 |
| R0203 | D-48C | 50 | 1.73 | 10.00 |
| R0204 | D-91A | 50 | 0.44 | 10.34 |
| R0204 | D-91B | 50 | 0.37 | 6.67 |
| R0204 | D-91C | 50 | 0.15 | 11.29 |
| R0205 | D-1A | 50 | 0.51 | 10.81 |
| R0205 | D-1B | 50 | 1.89 | 4.76 |
| R0205 | D-1C | 50 | 1.13 | 0.00 |
| R0206 | D-55A | 50 | 0.43 | 18.03 |
| R0206 | D-55B | 50 | 0.16 | 10.77 |
| R0206 | D-55C | 50 | 0.10 | 14.29 |
4/ (octahydro-4,7-methano-1H-indenyl) methyl acrylate (2000) | R0301 | D-47A | 50 | 0.31 | 16.13 |
R0301 | D-47B | 50 | 0.83 | 11.86 | |
R0301 | D-47C | 50 | 0.57 | 12.90 | |
| R0302 | D-30A | 50 | 2.63 | 4.41 |
| R0302 | D-30B | 50 | 1.70 | 8.62 |
| R0302 | D-30C | 50 | 1.71 | 9.21 |
| R0303 | D-69A | 50 | 0.23 | 4.69 |
| R0303 | D-69B | 50 | 0.19 | 7.94 |
| R0303 | D-69C | 50 | 0.40 | 7.94 |
| R0304 | D-40A | 50 | 0.82 | 20.63 |
| R0304 | D-40B | 50 | 0.16 | 19.40 |
| R0304 | D-40C | 50 | 0.08 | 16.18 |
| R0305 | D-5A | 50 | 0.09 | 3.77 |
| R0305 | D-5B | 50 | 0.19 | 7.94 |
| R0305 | D-5C | 50 | 0.08 | 9.84 |
| R0306 | D-49A | 50 | 0.49 | 5.00 |
| R0306 | D-49B | 50 | 0.55 | 5.00 |
| R0306 | D-49C | 50 | 0.51 | 5.08 |
5/ EMS (200) | R0401 | D-13A | 50 | 5.86 | 14.29 |
| R0401 | D-13B | 50 | 4.71 | 14.08 |
| R0401 | D-13C | 50 | 3.24 | 11.48 |
| R0402 | D-84A | 50 | 9.14 | 3.70 |
| R0402 | D-84B | 50 | 12.50 | 5.36 |
| R0402 | D-84C | 50 | 9.48 | 3.45 |
| R0403 | D-11A | 50 | 4.57 | 3.70 |
| R0403 | D-11B | 50 | 3.29 | 5.08 |
| R0403 | D-11C | 50 | 9.54 | 6.45 |
|
|
|
|
|
|
NE-NC | Not evaluated due to no cells |
EMS | Ethyl Methanesulfonate |
Historical Control Ranges: Comet Assay Data
Data generated from studies performed within the GLP laboratory, by GLP trained staff, whether a claim of GLP compliance was made or not, were included in the compilation of the historical control ranges without bias.
RAT LIVER COMET HISTORICAL CONTROL RANGES | |||
Vehicle Control Data | |||
Tail Intensity (%) | Hedgehogs (%) | ||
Number of Animals | 161 | 161 | |
Mean | 0.41 | 1.52 | |
Standard Deviation | 0.45 | 1.35 | |
Observed Range | Minimum | 0.01 | 0.00 |
Maximum | 2.37 | 7.89 | |
95% Reference Range | Lower Limit | 0.04 | 0.00 |
Upper Limit | 1.80 | 5.36 | |
Positive Control Data | |||
Tail Intensity (%) | Hedgehogs (%) | ||
Number of Animals | 82 | 82 | |
Mean | 26.43 | 1.57 | |
Standard Deviation | 7.92 | 1.40 | |
Observed Range | Minimum | 9.52 | 0.00 |
Maximum | 43.42 | 5.98 | |
95% Reference Range | Lower Limit | 10.53 | 0.00 |
Upper Limit | 37.00 | 5.41 | |
Range compiled Aug 2020; generated from 25 experiments (vehicle data) or 26 experiments (positive data) analysed between September 2018 and August 2020 |
RAT STOMACH COMET HISTORICAL CONTROL RANGES | |||
Vehicle Control Data | |||
Tail Intensity (%) | Hedgehogs (%) | ||
Number of Animals | 45 | 45 | |
Mean | 1.40 | 4.71 | |
Standard Deviation | 2.18 | 3.11 | |
Observed Range | Minimum | 0.15 | 0.60 |
Maximum | 11.46 | 14.05 | |
95% Reference Range | Lower Limit | 0.16 | 1.04 |
Upper Limit | 8.29 | 12.63 | |
Positive Control Data | |||
Tail Intensity (%) | Hedgehogs (%) | ||
Number of Animals | 21 | 21 | |
Mean | 12.68 | 5.50 | |
Standard Deviation | 4.36 | 2.84 | |
Observed Range | Minimum | 4.18 | 1.23 |
Maximum | 20.54 | 10.93 | |
95% Reference Range | Lower Limit | N/A | N/A |
Upper Limit | N/A | N/A | |
Range compiled Aug 2020; generated from 7 experiments (vehicle data) or 6 experiments (positive data) analysed between September 2018 and August 2020 |
RAT DUODENUM COMET HISTORICAL CONTROL RANGES | |||
Vehicle Control Data | |||
Tail Intensity (%) | Hedgehogs (%) | ||
Number of Animals | 50 | 50 | |
Mean | 0.95 | 5.95 | |
Standard Deviation | 0.86 | 3.94 | |
Observed Range | Minimum | 0.14 | 0.49 |
Maximum | 4.50 | 20.71 | |
95% Reference Range | Lower Limit | 0.20 | 0.54 |
Upper Limit | 3.14 | 13.22 | |
Positive Control Data | |||
Tail Intensity (%) | Hedgehogs (%) | ||
Number of Animals | 27 | 27 | |
Mean | 11.29 | 6.32 | |
Standard Deviation | 3.09 | 3.62 | |
Observed Range | Minimum | 3.19 | 2.01 |
Maximum | 17.49 | 16.67 | |
95% Reference Range | Lower Limit | N/A | N/A |
Upper Limit | N/A | N/A | |
Range compiled Aug 2020; generated from 9 experiments analysed between December 2018 and August 2020 |
Applicant's summary and conclusion
- Conclusions:
- It is concluded that, under the conditions of this Comet assay, (octahydro-4,7-methano-1H-indenyl) methyl acrylate did not induce DNA strand breaks in the liver, stomach or duodenum of male Sprague Dawley rats administered up to 2000 mg/kg/day (the maximum recommended dose for in vivo Comet studies).
- Executive summary:
The in vivo alkaline comet (single cell gel electrophoresis) assay is used for the detection of DNA strand breaks (apparent as an increase in DNA migration) in cells or nuclei isolated from tissues of animals that have been exposed to potentially genotoxic material(s). Under alkaline conditions (>pH 13), the comet assay can detect single and double stranded breaks, resulting, for example, from direct interactions with DNA, alkali labile sites or as a consequence of transient DNA strand breaks resulting from DNA excision repair. These strand breaks may be repaired, resulting in no persistent effect, may be lethal to the cell, or may be fixed into a mutation resulting in a permanent viable change. They may also lead to chromosomal damage which is also associated with many human diseases including cancer.
(octahydro-4,7-methano-1H-indenyl) methyl acrylate was tested for its potential to induce DNA strand breaks in the liver, stomach and duodenum of treated rats. As there was no strand break induction observed in any of the somatic tissues, the gonad was not assessed.
There were no dose-related increases in %hedgehogs in liver, stomach or duodenum, thus demonstrating that treatment with (octahydro-4,7-methano-1H-indenyl) methyl acrylate did not cause excessive DNA damage that could have interfered with comet analysis.
Animals treated with (octahydro-4,7-methano-1H-indenyl) methyl acrylate at all doses exhibited group mean tail intensities that were similar to the concurrent vehicle control group and that fell within the 95% reference range of the laboratory's historical vehicle control data. There were no statistically significant increases in tail intensity for any of the groups receiving the test article, compared to the concurrent vehicle control, with no evidence of a dose response.
These data were considered clearly negative in the liver, stomach and duodenum.
It is concluded that, under the conditions of this comet assay, (octahydro-4,7-methano-1H-indenyl) methyl acrylate did not induce DNA strand breaks in the liver, stomach or duodenum of male Sprague Dawley rats administered up to 2000 mg/kg/day (the current maximum recommended dose for in vivo Comet studies).
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