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EC number: 273-707-7 | CAS number: 69011-69-4 A scum formed on the surface of molten cadmium.
- 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: inhalation
Administrative data
- Endpoint:
- sub-chronic toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- No information
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: reliable without restriction. Well documented and scientifically acceptable. Method comparable to OECD Guideline.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 413 (Subchronic Inhalation Toxicity: 90-Day Study)
- Deviations:
- yes
- Principles of method if other than guideline:
- A study was conducted to determine the effects of sub-chronic exposure of the test material on the respiratory system and Cd distribution in F344 rats. The test material was administered 6 h and 20 min/d and 5 d/wk for 13 wk at 0, 0.025, 0.05, 0.1, 0.25 or 1 mg CdO/m3 to groups of 10 rats/sex/dose. Animals were observed twice daily for mortality and signs of toxicity and were weighed on Day 1, weekly thereafter and on the day of necropsy with clinical signs being observed daily. Following organs were weighed at necropsy: heart, right kidney, liver, lungs, spleen, right testis and thymus. Additionally, Cd distribution study and influence on blood pressure was evaluated.
- GLP compliance:
- yes
- Remarks:
- in compliance with United States FDA GLP regulations (21 CFR, Part 58)
- Limit test:
- no
Test material
- Reference substance name:
- Cadmium oxide
- EC Number:
- 215-146-2
- EC Name:
- Cadmium oxide
- Cas Number:
- 1306-19-0
- IUPAC Name:
- oxocadmium
- Details on test material:
- -Name of the test material: CdO
SOURCE: Lot 110383 from Johnson Matthey Aesar Group (Seabrook, NH).
PURITY: Purity : 99.4 % ( 0.6 % )
Impurities : 400 ppm chlorine, all other impurities detected totaled less than 263 ppm
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Simonsen Laboratories (Gilroy, CA)
- Age at study initiation: 6 wk old
- Weight at study initiation: M: 101-104 g (mean body weight per group); F: 92-94 g (mean body weight per group)
- Housing: in individual cages within the exposure chambers
- Diet : NIH-07 Open Formula Diet (Zeigler Brothers, Inc., Gardners, PA) in pellet form
- Water : City water (Richland, WA), ad libitum
- Acclimation period: 12-15 d
ENVIRONMENTAL CONDITIONS
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: unchanged (no vehicle)
- Remarks on MMAD:
- MMAD / GSD: MMAD = 1.1 - 1.6 µm
- Details on inhalation exposure:
- Particle size: MMAD = 1.1 - 1.6 µm
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Concentrations were monitored automatically (measured concentrations within 85% of nominal conc)
- Duration of treatment / exposure:
- 13 wk
- Frequency of treatment:
- 6 h and 20 min/d; 5 d/wk
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 0.025, 0.05, 0.1, 0.25 or 1 mg CdO/m3
Basis:
nominal conc.
- No. of animals per sex per dose:
- 10 M and 10 F per dose and control
- Control animals:
- yes
- Details on study design:
- Sacrificed after 13 weeks of exposure
- Positive control:
- None
Examinations
- Observations and examinations performed and frequency:
- Clinical observations performed and frequency:
Animals were observed twice daily for mortality and signs of toxicity and were weighted on Day 1, weekly thereafter and on the day of necropsy.
Clinical observations were recorded daily. - Sacrifice and pathology:
- Autopsy: Organs examined at necropsy (macroscopic and microscopic): complete necropsies were performed.
Following organs were weighed: heart, right kidney, liver, lungs, spleen, right testis and thymus. - Other examinations:
- Additional analyses: Cd distribution studies and Influence on blood pressure
- Statistics:
- organ and body weight data, which have approximately normal distributions, were analyzed with the parametric multiple comparison procedures of
Williams (1971, 1972) and Dunnett (1955). Clinical pathology, spermatid, epididymal spermatozoa data and Cd tissue concentrations were analyzed
with the nonparametric multiple comparisosn methods of Shirley (1977) and Dunn (1964). Jonckheere's test (Jonckheere 1954) was used to assess
the significance of dose-response trends and to determine whether a trend-sensitive test (Williams' or Shirleys' test) was more appropriate for
pairwise comparisons than a test that does not assume a monotonic dose-response (Dunnett's or Dunn's test). Trend-sensitive tests were used when Jonckheere's test was significant at a P-value less than 0.1. For indirect systolic blood pressure measurements, a one-way analysis of variance test
(Weter et al, 1985) was used to assess dose-response and time-response trends. For analysis of vaginal cytology data, because the data are
proportions (the proportion of the observation period that an animal was in a given estrous stage), an arcsine transformation was used to bring the
data into closer conformance with normality assumptions. Treatment effects were investigated by applying a multivariate analysis of variance
(Morrison, 1976) to the transformed data to test for simultaneous equality of measurements across dose levels.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- effects observed, treatment-related
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- not specified
- Histopathological findings: neoplastic:
- not specified
- Details on results:
- TOXIC RESPONSE/EFFECTS BY DOSE LEVEL:
Body weight: the final mean body weights and mean body weight gains of male and female rats in the highest exposure groups were notably lower than those of the control group (final weight relative to controls (%): 93).
Food/water consumption: no information
Description, severity, time of onset and duration of clinical signs: rats: nasal discharge in males and females. In females, the frequency of this sign increased with increasing exposure concentration.
Ophtalmologic findings incidence and severity: no information
Hematological findings incidence and severity: reticulocyte numbers were greater in exposed females (0.025 mg/m3 and higher groups) than in the controls at day 24, indicating a bone marrow response. However, there were no consistent changes indicating anaemia.
Clinical biochemistry findings incidence and severity: changes in rats were minor, sporadic and not considered significant Mortality and time to death:all rats survived until the end of the study.
Gross pathology incidence and severity: rats: enlargement and paleness of the tracheobronchial and mediastinal lymph nodes
Organ weight changes: rats: significant differences in organ weights from control values occurred in the three highest exposure groups: 0.1, 0.25 or 1 mg/m3
Histopathology incidence and severity:
Selected histopathologic lesions for male and female F344/N rats in the 13-week inhalation study of CdO (NTP Report, 1995) (See table 1)
MEASUREMENTS OF BLOOD PRESSURE:
There were no biologically significant effects of cadmium oxide exposure on blood pressure measurements at any time point. There were statistically significant differences in females in the 0.25 and 1 mg/m3 groups at Week 13. However, these differences were considered to be anomalies for the following reasons: the 0.25 and 1 mg/m3 group means (120 to 130 mm) were within the normal range, the control value (102 mm) was on the low end of the normal range, a dose-response relationship was not present, and the data for females at the initial time point varied considerably from one group to another. Using a one-way analysis of variance test (Weter et aL, 1985), a significant difference among female rats was found at the initial time point. When the data were standardized by the initial time point data, there were no significant differences in dose-response or time-response for blood pressure measurements.
CADMIUM DISTRIBUTION STUDY:
Cadmium accumulation increased with exposure concentration at all time points, but the increases were not proportional to the increases in exposure concentration. Cadmium lung concentration did not achieve steady state over the course of the study. Cadmium concentrations increased with increasing exposure concentration in the kidney at all time points and in the blood at Day 9, Day 30, and Week 13. Concentrations of cadmium in the lung and kidney were significantly greater than those of the controls for all exposure groups at every time point. Cadmium concentrations in the blood of rats exposed to 1 mg/m3 cadmium oxide were significantly greater than the controls after just three days of exposure and remained so throughout the study. For rats in the 0.25 mg/m3group, cadmium concentrations in the blood were significantly greater than in the controls after 9 days of exposure and throughout the study. Further details on tissue levels of cadmium are reported by Dill et al (1994).
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 0.025 mg/m³ air
- Sex:
- male/female
- Dose descriptor:
- LOAEL
- Effect level:
- 0.05 mg/m³ air
- Sex:
- male/female
- Basis for effect level:
- other: lung effects
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Applicant's summary and conclusion
- Conclusions:
- Treatment-related respiratory tract lesions were found in the lungs, nose and larynx of FN344/N rats exposed by inhalation to CdO for 13 wk.
- Executive summary:
A study was conducted to determine the effects of sub-chronic exposure of the test material on the respiratory system and Cd distribution in F344 rats.
The test material was administered 6 h and 20 min/d and 5 d/wk for 13 wk at 0, 0.025, 0.05, 0.1, 0.25 or 1 mg/m3 to groups of 10 rats/sex/dose. Animals were observed twice daily for mortality and signs of toxicity and were weighed on Day 1, weekly thereafter and on the day of necropsy with clinical signs being observed daily. Following organs were weighed at necropsy: heart, right kidney, liver, lungs, spleen, right testis and thymus. Additionally, Cd distribution study and influence on blood pressure was evaluated.
Available results indicate enlargement and paleness of the tracheobronchial and mediastinal lymph nodes in the treated groups. Overall, treatment-related respiratory tract lesions were found in the lungs, nose and larynx of FN344/N rats exposed by inhalation to CdO for 13 wk.
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