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EC number: 208-175-7 | CAS number: 513-88-2
- 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- disregarded due to major methodological deficiencies
- Study period:
- 1993
- Reliability:
- 4 (not assignable)
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 993
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- 1,1-dichloroacetone
- EC Number:
- 208-175-7
- EC Name:
- 1,1-dichloroacetone
- Cas Number:
- 513-88-2
- Molecular formula:
- C3H4Cl2O
- IUPAC Name:
- 1,1-dichloropropan-2-one
- Reference substance name:
- 1,1-Dichloro-2-Propanone
- IUPAC Name:
- 1,1-Dichloro-2-Propanone
- Test material form:
- other: colourless oily liquid
- Details on test material:
- purity 98%
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Charles River Laboratories, 70 days old, 200-300 g.
Acclimatisation: 2 weeks.
26°C, 40-50% humidity, 12:12 light:dark cycle.
Purina certified Chow 5002, tap water ad libitum.
Identified by ear tag, randomized into treatment groups.
Start weight female 255-263 g, male 406-423 g.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- 1 mL corn oil per kg body weight
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- GC analysis
- Duration of treatment / exposure:
- 90 days
- Frequency of treatment:
- daily for 90 days
Doses / concentrations
- Remarks:
- Doses / Concentrations:
10, 20, 40, 80 mg/kg/day
Basis:
other: actual in vehicle
- No. of animals per sex per dose:
- 10 male and 10 female
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- all rats were observed twice daily, bodyweights recorded weekly, water consumption three times a week, food consumption weekly
- Positive control:
- no
Examinations
- Observations and examinations performed and frequency:
- The following organs and tissues were collected at necropsy and preserved in 10%
buffered formalin: skin, mammary glands, thigh muscle, sciatic nerve, mandibular lymph
nodes, mesenteric lymph nodes, femur (including bone marrow), tongue, salivary gland,
thymus, trachea, lung with bronchi, esophagus, stomach, duodenum, jejunum, ileum,
cecum, colon, rectum, liver, pancreas, spleen, kidneys, adrenals, urinary bladder, seminal
vesicles, prostate, testes (including epididymis), ovaries, uterus, preputial or clitoral
glands, Zymbal's gland, nasal turbinates, brain, pituitary, thyroiWparathyroid, heart, and
aorla. Subsequently, tissues taken from 5 males and 5 females of the control group as
well as all surviving animals in the highest dose groups were trimmed, embedded in
paraffin, sectioned at 5 pm, and stained with hematoxylin and eosin. The tissues were
initially examined by a veterinary pathologist and subsequently, the liver, kidneys, and
stomach, (identified as possible target organs) were examined in all of the lower dose
groups.
Inflammatory and degenerative lesions were graded according to severity using a
scale of one to four (minimal, mild, moderate, or marked)and the data were tabulated by
individual animal and then summarized by group. - Sacrifice and pathology:
- Animals were euthanized following blood collection via exsanguination and
immediately necropsied. The necropsy included gross examination of the animals'
external surface and orifices, external surface of the brain, all organs, and the thoracic,
abdominal. and pelvic cavities. The adrenal glands, brain (including the brain stem),
gonads, heart, kidneys, liver, lungs, spleen, and thymus were weighed. - Other examinations:
- The following serum clinical chemistry determinations were accomplished using a
Baker Encore centrifugal analyzer: blood urea nitrogen (BUN), calcium (CA), creatinine
(CRE), total cholesterol (CHO), glucose (GLU), lactate dehydrogenase (LDH), inorganic
phosphorus (PO4), aspartate aminotransferase (AST), and alanine aminotransferase
(ALT). Appropriate normal and abnormal whole blood and serum controls were evaluated
at each assay. - Statistics:
- Data were analyzed by sex using a one-factor (dose) analysis of variance (ANOVA)
method to test for normal distribution of data (p <= 0.05), the difference between the
control and treatment groups was further analyzed, using the Tukey's multiple
comparison procedure for overall differences. Due to the high variability of some of the
clinical chemistry and organ weight measures, a nonparametric analysis of variance
procedure, i.e.the Kruskal-Wallis test, was also employed to determine differences
among the dose groups. The statistical significance of histopathological occurrences was
tested using Fisher's One-tail test comparing each treatment group to controls.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- No rats died during the study.
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- No rats died during the study.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- decrease
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- no effect
- Haematological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- increase: serum enzymes
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- increase: serum enzymes
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- increase for liver and kidneys
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- All gross lesions were considered to be incidental findings and not related to DCP exposure.
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- liver, forestomach, kindneys
- Histopathological findings: neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- bile duct hyperplasia
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Groups of 10 male and 10 female Sprague-Dawley rats were administered 1,1-Dichloro-2-Propanone in corn oil by gavage at 0, 10, 20, 40, or 80 mg/kg/day for 90 consecutive days. No treatment related mortality was observed during the study, however: liver, forestomach and kidney toxicity was evident. Based on liver lesions and biochemical changes it was concluded that there was no experimentally definable NOAEL.
- Executive summary:
Oral (gavage) administration of DCP in corn oil at doses of 0, 10, 20, 40, and 80
mg/kg/day for 90 days to male and female rats did not affect mortality however liver and
forestomach toxicity were observed in both sexes while an increased incidence of kidney
changes were apparent only in the males.
The liver changes included a dose-dependent increase in cytoplasmic alteration,
cytomegaly, karyomegaly, and bile duct hyperplasia which occurred without substantial
hepatocellular necrosis and were probably due to a direct treatment-related
metabolic/biochemicaI stimulus with enhanced cellular metabolism and enzyme induction.
The hepatic cytomegaly present in the highest dose groups was consistent with the
increased liver weights that were observed in both females and males.
While the microscopic changes noted in the liver appeared similar in females and
males, there were differences in the serum enzyme (ALT, AST, and LDH) activities.
These enzymes were elevated in females, but decreased in males. While the mechanism
responsible for this sex difference cannot be stipulated, this paradoxical suppression of
metabolic enzymes is probably not an artifact of the kinetic assays since similar findings
have been documented in prior studies with related chemicals (Bercz, unpublished
results).
DCP induced hyperkeratosis and epithelial hyperplasia of the forestomach in all
treated animals at 80 mg/kg/day and in over 80% of those in the 40 mg/kg/day groups.
There appears to be a sharp threshold for this effect since these changes were not
observed at the two lowest doses or in the controls. .Ulcerations of the forestomach were
obsewed only at the highest dose level in both females and males. Lesions of this
nature, in which there is a noted increase in the number of cells and keratin production,
are generally indicative of direct chemical irritation to the mucosal surface.
The incidence of spontaneous progressive nephropathy which is known to be
caused in rats by stress or genetic susceptibility.(' displayed a treatment related
incidence increase in the high dose males; however, it appeared randomly in females.
The results of this study clearly indicate that the liver and forestomach are primary
target organs for DCP toxicity with microscopic lesions being observed in both male and
female rats. In addition, statistically significant changes in select serum enzymes were
found at all dose levels. Based on the presence of the various changes at all dose levels,
it was concluded that there was no NOAEL in this study.
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