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EC number: 204-278-6 | CAS number: 118-79-6
- 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
- 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:
- short-term repeated dose toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- disregarded due to major methodological deficiencies
- Study period:
- 1977
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- This study was conducted before current guidelines were in place and as such does not meet current standards for testing protocols. The study uses whole-body exposure so that oral dosing is expected to confound the results, and there is no information on the size of the particles generated. Other than weight change, there were no results that differed from control and would therefore offer an index of the toxicologic response to the test compound.
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:
- 1 977
- Report date:
- 1977
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- Three groups of 10 albino rats, 5 males and 5 females, were exposed to either 0, 0.1, or 1.0 mg/l dust for 6 hours per day, 5 days per week for 3 weeks (15 exposure periods). Mortality, cageside observations ,and body weight were taken for all animals, and haematology, clinical chemistry, and urinalysis were noted for selected animals for all groups. A necropsy was performed on all animals, including histopathology on selected tissues and organs from the control and high dose groups.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- 2,4,6-tribromophenol
- EC Number:
- 204-278-6
- EC Name:
- 2,4,6-tribromophenol
- Cas Number:
- 118-79-6
- Molecular formula:
- C6H3Br3O
- IUPAC Name:
- 2,4,6-tribromophenol
- Details on test material:
- Physical description: beige crystalline material, no lot number given
Analytical data for two lot numbers of tribromophenol are listed:
Lot 02136A - 99.5% pure, melting point 94.1 degrees C, appearance: contained brown specks
Lot 10196 - 99.7% pure, melting point 94.0 degrees C, appearance: clear
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: Albino Charles River COBS strain
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Young adult rats were selected from a 5 day observation period, after being judged to be healthy. The animals were housed in stainless steel cages and given Wayne LAB_BLOX for Rats (Allied Mills, Inc., Chicago IL) plus water ad libitum except during the inhalation exposure period. There are no further details on holding or handling conditions.
Administration / exposure
- Route of administration:
- inhalation: dust
- Type of inhalation exposure:
- whole body
- Vehicle:
- clean air
- Remarks on MMAD:
- MMAD / GSD: unknown
- Details on inhalation exposure:
- Comparatively few details are available.
The inhalation chambers had a capacity of 80 L, and animals were confined individually in the chambers. Control animals received no dust exposure. Test dust was generated with specially designed dust-shaking mechanisms capable of producing steady concentrations over a long period of time. Air was clean and dry (dewpoint -40 degrees C) when passed through the test powder. The resulting air and dust mixture was introduced into the exposure chambers at the top center and exhausted at the bottom of the exposure chambers. Air flow rats were measured with rotameters connected upstream of the dust feeders. The rotatmeters were calibrated with a bubble meter after completion of each exposure. Temperature and pressure of the chamber were recorded. Concentrations of test dust present in the exposure chamber were determined by sampling the test atmosphere in the breathing zone of the animals being exposed. The total weight of dust collected on a glass filter was divided by the total volume of air drawn through the filter during the sampling period. Air flow rates for sampling were regulated by calibrated limiting orifices. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analysis of the chamber atmosphere was conducted by a Hewlett-Packard 5711 gas chromatograph with dual FID and 3% Dexsil 300 on 90/100 mesh Anakrom Q column using Gelman Type A filters.
Chamber air was passed throiugyh the Gelman filter at a rate of 4 L/min for 2.5 minutes (total of 10 liters). The filter samples were weighed, then mixed with 10 ml of methanol to extract the tribromophenol. A 3 uL volume of each extraction was injected into the GC and the concentration in mg/ml was obtained from the calibrating graph. - Duration of treatment / exposure:
- 6 hours per day
- Frequency of treatment:
- 5 days per week, for 3 weeks
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 0.1, 1.0 mg/L
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5 males and 5 females per dose group = 30 rats
- Control animals:
- yes, sham-exposed
- Details on study design:
- - Dose selection rationale: not stated
- Rationale for animal assignment (if not random): random - Positive control:
- None
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily
- Cage side observations checked in table [No.?] were included. No data
DETAILED CLINICAL OBSERVATIONS: No
BODY WEIGHT: Yes
- Time schedule for examinations:before first exposure and weekly thereafter
FOOD CONSUMPTION:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No data
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at termination of study
- Anaesthetic used for blood collection: No data
- Animals fasted: No data
- How many animals: 3 per sex per group
- Parameters checked in table [No.?] were examined. Tables VI - XI: Total leukocyte count, erythrocyte count, hemoglobin concentration, hematocrit, differential leukocyte count (neutrophils, lymphocytes, monoytes, eosinophils, basophils), erythrocytes indices (MCV, MCH, MCHC)
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: at termination of study
- Animals fasted: yes
- How many animals: 3 per sex per group
- Parameters checked in table [No.?] were examined. Tables XII - XIII: Glucose concentration, blood urea nitrogen, SAP activity, SGPT activity
URINALYSIS: Yes
- Time schedule for collection of urine: day 0 and at termination of treatment
- Metabolism cages used for collection of urine: Yes
- Animals fasted: No data
- Parameters checked in table [No.?] were examined. Table XIV-XVII: blood, ketones, glucose, proteins, pH, leukocytes, erythrocytes, crystals - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes (see Table X)
HISTOPATHOLOGY: Yes (see Table X) - Other examinations:
- No further information required
- Statistics:
- None reported
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- One male low dose and one female high dose animal died before the end of the study.
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- One male low dose and one female high dose animal died before the end of the study.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Females exposed to low dose, and males exposed to the high dose, exhibited lower mean body weight gains when compared with those of untreated controls.
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- At necropsy, 4/5 male rats and all 5 female rats from the high treatment gropu were emaciated. An area of tan discoloration was observed on the kidney of 1 male rat in the high treatment group, and an area described as fibrotic was observed in the liver
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- Histopathologic evaluation of rats in the high treatment group revealed dilation of renal tubules in 3/5 rats of each sex, and a solitary area of submassive hepatic necrosis in 1 female rat.
- Histopathological findings: neoplastic:
- not examined
- Details on results:
- Treatment-related effects included reduced weight gain in males and females at 1 mg/l. Other treatment-related effects were hypoactivity and salivation on all exposure days (except Day 4 in the low dose group), and isolated instances of red nasal discharge and lacrimation.
Effect levels
open allclose all
- Dose descriptor:
- NOAEC
- Effect level:
- 0.1 mg/L air
- Based on:
- act. ingr.
- Sex:
- male/female
- Basis for effect level:
- other: see 'Remark'
- Dose descriptor:
- LOAEC
- Effect level:
- 1 mg/L air
- Based on:
- act. ingr.
- Sex:
- male/female
- Basis for effect level:
- other: Effects seen in kidney, liver, and on body weight.
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Treatment group, number of animals affected | ||||
Observation | Gender | Control | 0.1 mg/l | 1.0 mg/l |
Hypoactivity | Male | - | 10 | 10 |
Female | - | 10 | 10 | |
Salivation | Male | - | 10 | 10 |
Female | - | 10 | 10 | |
Lacrimation | Male | - | 1-2 daily | 1-3 daily |
Female | - | |||
Body weight at Day 21 | Male | 345 g | 343 g | 242 g |
Female | 230 g | 216 g | 172 g | |
Body weight change | Male | 113 g | 90 g | -16 g |
Female | 35 g | 17 g | -22 g | |
Dilation of renal tubules | Male | 0 | 0 | 3/5 |
Female | 0 | 0 | 3/5 | |
Discolored kidney spot | Male | 0 | 0 | 1 |
Female | 0 | 0 | 0 | |
Fibrotic area on liver | Male | 0 | 0 | 0 |
Female | 0 | 0 | 1 | |
Hepatic necrosis (submassive) | Male | 0 | 0 | 0 |
Female | 0 | 0 | 1 |
Applicant's summary and conclusion
- Conclusions:
- In this study, inhalation of 1.0 mg/l air containing 2,4,6-tribromophenol dust for 21 days resulted in reduced weight gain, dilation of kidney tubules, and individual liver effects. These effects were not seen at 0.1 mg/l under the same experimental conditions. The kidney and liver are organs seen to be affected at high doses after other routes of exposure, so this study is consistent with other studies with systemic expsoure to tribromophenol. The NOEL is determined to be 0.1 mg/l (no mg/kg bw calculated), and the LOEL is 1.0 mg/l.
- Executive summary:
Five rats/gender/dose were repeatedly exposed for 21 days (15 doses total) to 2,4,6 -tribromophenol dust in individual whole-body inhalation chambers. The doses were 0, 0.1, and 1.0 mg/l clean, dry air, and the exposure was for 6 hours/day, 5 days/week. Data was taken for physical reactions from dosing, body weight, maematology, clinical chemistry, urinalysis, gross pathology, and histopathology. There was one low dose male and one high dose female that died after 10 and 11 doses, respectively. Animals in both treatment groups exhibited hypoactivity, salivation, lacrimation, and red nasal discharge during testing. Hypoactivity, lacrimation, and nasal discharge are symptoms consistent with exposure to dust particulates without regard to the compound itself. Salivation has been noted as a transient symptom after exposure to tribromophenol specifically. Low dose animals showed similar weight gain to controls, but high dose animals exhibited visibly lower weight gain than controls. Additionally, dilation of renal tubules was seen in 3 of 5 high dose animals of both genders, and one high dose female had two liver lesions (submassive necrosis and fibrosis).
Based on the above observations, the NOAEL is set at 0.1 mg/l (transient salivation is not considered adverse), and the LOAEL is set at 1.0 mg/l. This study is considered adequate to determine target organs and order of magnitude to find effects, but does not meet current standards for study design or documentation of results. This dose is also expected to be inaccurate based on oral exposure from grooming during and after the whole-body exposure in the inhalation chamber.
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