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EC number: 237-335-9 | CAS number: 13752-51-7
- 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 germ cell study: cytogenicity / chromosome aberration
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 980
- Report date:
- 1980
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 478 (Genetic Toxicology: Rodent Dominant Lethal Test)
- Version / remarks:
- FDRL Proposol No. 79062-B, further defined in FDRL Protocol 6477
- GLP compliance:
- yes
- Type of assay:
- rodent dominant lethal assay
Test material
- Reference substance name:
- 4-[(morpholinothio)thioxomethyl]morpholine
- EC Number:
- 237-335-9
- EC Name:
- 4-[(morpholinothio)thioxomethyl]morpholine
- Cas Number:
- 13752-51-7
- Molecular formula:
- C9H16N2O2S2
- IUPAC Name:
- morpholin-4-yl morpholine-4-carbodithioate
- Reference substance name:
- Cure-Rite® 18; commercial
- IUPAC Name:
- Cure-Rite® 18; commercial
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Blue Spruce Farms Inc.
- Age at study initiation: not stated.
- Weight at study initiation: 307 - 329 grams mean weight at week 1.
- Assigned to test groups randomly: yes
- Fasting period before study: no
- Housing: 1 male per wire mesh cage, 2 females per cage.
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 10 days
IN-LIFE DATES: From: 31 March 1980 To: 18 June 1980
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Corn Oil.
- Details on exposure:
- All housed male rats were gavaged at the appropriate dose for 56 consecutive days.
Positive control animals were dosed with Triethylenemelamine via intraperitoneal injection on the last day of the treatment period. - Duration of treatment / exposure:
- Male rats were dosed for 56 consecutive days before being housed with the female rats.
- Frequency of treatment:
- Daily
- Post exposure period:
- One week for males housed with two females to allow for mating. Then the two females were replaced by two more females for one week.
Thirteen days after the midpoint of each cohabitation, all females were sacrificed and subjected to uterine examination.
After the final mating period, three males per treatment group were randomly selected for necropsy.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Basis:
nominal conc.
0, 6.25, 12.5 and 25 mg/kg/day. TEM 0.25 mg/Kg/day
- No. of animals per sex per dose:
- 10 males per group, in 5 groups (labelled A, B, C, D, E).
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- triethylenemelamine
- Justification for choice of positive control(s):
- Route of administration: intraperitoneal injection on last day of treatment.
- Doses / concentrations: 0.25 m/Kg/Day.
Examinations
- Tissues and cell types examined:
- Male rats: The following tissues were preserved - adrenals, brain, kidneys, liver, spleen, lung/main bronchi, sciatic nerve/skeletal muscle, testes, seminal vesicles, epididymides, prostate, pancreas, spinal cord, stomach, altered tissues.
- Details of tissue and slide preparation:
- All tissues taken from males rats were weighed except for the sciatic nerve/skeletal muscle, pancreas and spinal cord. Organ/body weight ratios were calculated for each.
- Evaluation criteria:
- Female rats: uterine examination to evaluate percent pregnancy, implantation per pregnancy, pre-implantation losses, early fetal deaths per pregnancy, late fetal deaths per pregnancy, and percent early fetal deaths per dam.
- Statistics:
- The effects of mating and treatment and their interaction were analyzed statistically at a 0.05 level of significance. Percentages and proportions were
analyzed using 95% confidence intervals or by computation of exact probabilities. Continuous data were analyzed using a one-way completely random classification analysis of variance for fixed effects. When differences were indicated, the least significant differences test was then employed
to determine which group(s) differed from the control.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- Number of implantation sites in females from the test groups were comparable to the control group. The positive control mated females had a significantly lower number of implantation sites per females.
The mean percent of pre-implantation losses were similar to the control groups and fall within accepted limits as presented by FDRL. The positive control was significantly higher.
Mean number of early fetal deaths per pregnancy and the mean percent of early fetal deaths were comparable to the control groups. The positive control was significantly higher.
Any other information on results incl. tables
Pregnancy rates overall range: 75 - 95%
Control group (corn oil) - 85%
TEM positive control - 90%
6.25 mg/Kg Curerite 18 - 85%
12.5 mg/Kg Curerite 18 - 95%
25.9 mg/Kg Curerite 18 - 95%
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The data was judged to indicate that Cure-rite 18 failed to produced dominant lethal mutations. - Executive summary:
The present dose levels of Curerite 18 were able to produce a dose related decrease in body weight gains over the 56 day dosing period. It also showed that Curerite 18 did not alter pregnancy or early fetal deaths. The alterations in implantation and preimplantation losses were judged to be related to a decrease in fertility for this group in the first mating. This is supported by the number of implants per dam and percentage preimplantation losses per dam for the high dose group fall into the normal range of values under FDRL limits.
Therefore, Curerite 18 is considered to not produce dominant lethal mutations.
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