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EC number: 202-739-6 | CAS number: 99-20-7
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 9. July 1997 - 12. November 1997
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 997
- Report date:
- 1997
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 475 (Mammalian Bone Marrow Chromosome Aberration Test)
- GLP compliance:
- yes
- Type of assay:
- mammalian bone marrow chromosome aberration test
Test material
- Reference substance name:
- Trehalose
- EC Number:
- 202-739-6
- EC Name:
- Trehalose
- Cas Number:
- 99-20-7
- Molecular formula:
- C12H22O11
- IUPAC Name:
- trehalose
- Test material form:
- solid: crystalline
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material:
50615
- Expiration date of the lot/batch:
not stated
- Purity test date: not stated
RADIOLABELLING INFORMATION (if applicable)
not applicable
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material:
room temperature, protected from Light
- Stability under test conditions: assumed stable
- Solubility and stability of the test substance in the solvent/vehicle:
soluble in water and assumed stable
- Reactivity of the test substance with the solvent/vehicle of the cell culture medium:
assumed stable
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
none
FORM AS APPLIED IN THE TEST (if different from that of starting material)
TYPE OF BIOCIDE/PESTICIDE FORMULATION (if applicable)
OTHER SPECIFICS:
Test animals
- Species:
- mouse
- Strain:
- Swiss Webster
- Details on species / strain selection:
- no further details, standard species for Assay
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Hollister CA
- Age at study initiation: Males: 6-7 weeks
Females: 7-8 weels
- Weight at study initiation: Males: 24.1-31.3 g
Females: 21.8-29.3 g
- Assigned to test groups randomly: randomly
- Fasting period before study: not specified
- Housing: no more than 5/cage
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 5 d
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 66 -72 °F
- Humidity (%): 46-54 %
- Air changes (per hr): not stated
- Photoperiod (hrs dark / hrs light): 12 / 12
IN-LIFE DATES: From: To:
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: water;
- Justification for choice of solvent/vehicle: common solvent in nature and for testing
- Concentration of test material in vehicle: depending on dose, 125 / 250 / 500 mg/mL
- Amount of vehicle (if gavage or dermal): not applicable
- Type and concentration of dispersant aid (if powder): not applicable
- Lot/batch no. (if required): not applicable
- Purity: - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Dose solutions were prepared by diluting weighted amounts of trehalose in sterile water for injection, USP. Dose preparation was mixed with a stir bar for approximately 45 minutes and then sonicated for approximately 5 minutes, before serial dilutions were prepared. - Duration of treatment / exposure:
- single dose
- Frequency of treatment:
- single dose
- Post exposure period:
- 24 or 48 hours
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw (total dose)
- Dose / conc.:
- 1 250 mg/kg bw (total dose)
- Dose / conc.:
- 2 500 mg/kg bw (total dose)
- Dose / conc.:
- 5 000 mg/kg bw (total dose)
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
- Justification for choice of positive control(s): not stated, but according to guideline
- Route of administration: intraperitoneal
- Doses / concentrations:
The positive control was prepared by adding 25 mg
of cyclophosphamide to sterile water. It was then
brought up to a volume of 10 mL. Dose
formulations were stored at room temperature until
used.
Examinations
- Tissues and cell types examined:
- bone marrow
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
not stated
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields):
1 dosage
DETAILS OF SLIDE PREPARATION:
At 24, or 48 hrs post-treatment, mice were
euthanized with C02 followed by cervical
disolcation. femurs were removed and three bone
marrow slides were prepared, fixed in absolute
methanol and stained with acridine orange.
METHOD OF ANALYSIS:
Two principal parameters were determined using 1
slide/animal: 1) the number of PCE among 200 total
erythrocytes (RBC) per animal, and 2) the number
of micronucleated RNA positive erythrocytes (PCE)
among a total of 2,000 PCE per animal.
Two principal parameters were determined using 1
slide/animal: 1) the number of PCE among 200 total
erythrocytes (RBC) per animal, and 2) the number
of micronucleated RNA positive erythrocytes (PCE)
among a total of 2,000 PCE per animal.
additional requirement that the micronuclei exhibit
the bright yellow fluorescence characteristic of
acridine orange stain. The data from a given slide
were registered directly to an IBM PC data file
during scoring (using the SRI-developed software
program MNSCORE). After analysis, the slides
were decoded and the data summarized by using a
decoding program in an IBM PC (using the SRIdeveloped
software program MNSUM).
OTHER: - Evaluation criteria:
- Positive. The test article was considered positive if 1 )there was a statistically
significant (p<0.05) increase in micronucleated PCE, 2) this increase was dose-related,
and 3) the micronucleated PCE frequency was greater than the mean historical
micronucleus vehicle frequency± 2 SD.
Negative. The test article was considered negative if the none of the criteria for a
positive or inconclusive response were met.
Inconclusive. The results were considered inconclusive if a statistically
significant increase in the micronucleated PCE frequency was observed that was either
not dose-related or was not greater the mean historical micronucleus frequency± 2 SD. - Statistics:
- Clinical Observations were not evaluated statistically. Body weights were
evaluated by the LABCAT computerized data capture system (Innovative Programming ·
Associates, Inc., Princeton, NJ; module BWT/CO v.4.64). One-way analysis of variance
(ANOVA) followed by Dunnett's test to compare each treated group with the vehicle
control group were performed. The probability level for all null hypothesis rejection was
p<0.05.
For the micronucleus assay, the data were analyzed separately for each gender and
each harvest time. The ratio of micronucleated PCEs to total PCEs and the ratio of PCEs
to total erythrocytes in percentages were calculated for each animal.
The frequency of micronucleated PCEs was statistically analyzed using the
Cochran-Armitage test (using the SRI-developed software COCHRAN) for trend in
binomial proportions, to determine if a significant dose-response relationship was present,
and the normal test for equality of binomial proportions (Kastenbaum and Bowman,
1970) to determine whether values for individual dose groups were statistically different
from those from vehicle controls (using the SRI-developed software package MNSUM).
These tests and their rationale are discussed in the ASTM Standard Guide for the Conduct
of Micronucleus in Mammalian Bone Marrow Erythrocytes and other publications
(ASTM Committee, 1988; Margolin et al., 1983).
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- In the micronucleus experiment, 10 mice per sex per dose group were treated with
a single i.p. dose of Trehalose at 1250, 2500, or 5000 mg/kg. Five mice per sex per dose.
group were sacrificed approximately 24, or 48 hours after treatment and bone marrow
was evaluated for cytotoxicity and micronucleus formation. A vehicle control group and
a cyclophosphamide positive control group were treated similarly (except for n=4 at 24
hrs in the cyclophosphamide positive control group) and evaluated concurrently with the
Trehalose-treated test groups. No statistically significant increases in micronucleated
PCE frequency was seen in any of the Trehalose-treated animals. As expected, the
frequency of micronucleated PCEs of male mice treated with cyclophosphamide was
statistically significant at the 24- and 48-hr harvest using the binomial proportions test.
The data from this experiment was considered acceptable because the frequency
of micronucleated PCEs in the vehicle control groups was within SRI's normal historical
mean± 2 SD (Appendix D), the administration of the cyclophosphamide positive control
resulted in a statistically significant elevation of micronucleated cells, and there were at
least three surviving animals of each sex in two or more dose groups with a PCE/RBC
ratio greater than or equal to 0.1.
Applicant's summary and conclusion
- Conclusions:
- In conclusion, Trehalose meets the criteria for a negative response in the mouse bone marrow micronucleus assay.
- Executive summary:
The genotoxic potential of Trehalose administered by intraperitoneal (ip) injection to
induce micronucleus formation in bone marrow erythrocytes was determined in Swiss-Webster
mice.
In the micronucleus experiment, 10 mice per sex per dose group were treated with a
single i.p. dose of Trehalose at 1250, 2500, or 5000 mg/kg. Five mice per sex per dose group
were sacrificed approximately 24, or 48 hours after treatment and bone marrow was evaluated for
cytotoxicity and micronucleus formation. A vehicle control group and a cyclophosphamide
positive control group were treated similarly and evaluated concurrently with the Trehalosetreated
test groups. There were no early deaths or significant clinical signs. No statistically
significant increases in micronucleated PCE frequency was seen in any of the Trehalose-treated
animals.
In conclusion, Trehalose meets the criteria established in the study protocol for a negative
response in the mouse bone marrow erythrocyte micronucleus assay.
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