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EC number: 203-427-2 | CAS number: 106-72-9
- 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
Endpoint summary
Administrative data
Description of key information
As the NOAEL of 300 mg/kg/d is well above the CLP guideline concentration values for specific target organ toxicity for repeat dose exposure, the substance can be considered not classified for this endpoint.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- February 14, 1989 - March 15, 1989
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Meets generally accepted scientific standards, well documented and acceptable for assessment
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 407 (Repeated Dose 28-Day Oral Toxicity Study in Rodents)
- Deviations:
- not specified
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- yes
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- One-hundred twenty-six (63 males and 63 females) 4-week-old Sprague-Dawley rats, Crl:CD•BR, •(birth date 1/02/89), were received from Charles River Laboratories, Raleigh, North Carolina, on January 31, 1989. The animals were housed individually in hanging stainless-steel, wire-mesh cages with Purina Certified Rodent Chowe 5002 and tap water available ad libitum.
The feed was analyzed by the manufacturer for concentrations of specified heavy metals, aflatoxin, chlorinated hydrocarbons, organophosphates, and specified nutrients. The water is routinely analyzed on a retrospective basis for specified pesticides, heavy metals and microbes. Results of all analyses of feed and water are on file with Hazleton Laboratories America, Inc. None of the possible contaminants in animal feed or water were considered to be at levels sufficient to interfere with this study. From initiation of dosing to study termination, environmental conditions were maintained within protocol-specified limits of temperature within 72 ± 6°F and the relative humidity within 50 ± 20%. Temperature and humidity were recorded using a sling psychrometer. A 12-hour light/12-hour dark cycle was maintained. - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- The test material was assumed to be 100% pure for purposes of dosage calculations. The calculated amount of test material was weighed out into a pre-calibrated container on an appropriate balance and the vehicle (corn oil) was added to reach the final volume. The purity of the test vehicle was assumed to be 100%. A stir bar was added to the contents and the container was placed on a magnetic stir-plate and the mixture was stirred for approximately five to seven minutes until a solution was achieved. Samples of fresh formulations and vehicle control solution from both the first day and last day of mixing were taken for stability and homogeneity analysis and sent to the sponsor.
The test mixtures were prepared fresh weekly and administered by gavage once daily, seven days a week, for 29 days. The dosing volume was based on a dosing factor of 10 ml/kg. - Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 29 days
- Frequency of treatment:
- administered by gavage once daily, seven days a week, for 29 days
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Remarks:
- Doses / Concentrations:
0 mg/kg/d (vehicle control)
Basis:
actual ingested - Dose / conc.:
- 300 mg/kg bw/day (nominal)
- Remarks:
- Doses / Concentrations:
300 mg/kg/d (low)
Basis:
actual ingested - Remarks:
- Doses / Concentrations:
1500 mg/kg/d (mid)
Basis:
actual ingested - Remarks:
- Doses / Concentrations:
3000 mg/kg/d (high)
Basis:
actual ingested - No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- As per guideline
- Positive control:
- No
- Observations and examinations performed and frequency:
- Observations and Records
Mortality and moribundity checks were made twice daily (morning and afternoon). Daily cage side observations for obvious indications of a toxic effect were recorded (approximately one hour post-dose) by exception. Body weights and food consumption were recorded weekly. Physical examinations were performed and detailed clinical observations were recorded at each weekly weighing interval. - Sacrifice and pathology:
- -Clinical Pathology-
Prior to initiation of dosing, ten animals per sex were selected at random from the pool of healthy animals available for study (identified as Group 5). These animals were fasted overnight and blood samples for baseline hematology and chemistry values were obtained by orbital sinus venipuncture under ketamine anesthesia. After blood collection the animals were euthanized and discarded without necropsy.
At termination all surviving animals were fasted overnight prior to necropsy. Animals were injected with ketamine and blood samples for haematology and chemistry were collected by orbital sinus venipuncture. The following haematology and clinical chemistry parameters were analyzed:
---Haematology---
leukocyte count (WBC)
erythrocyte count (RBC)
haemoglobin (HGB)
haematocrit (HCT)
platelet count (PLATELET)
leukocyte differential count
cell morphology
myeloid/erythroid ratio (M/E)
---Clinical Chemistry---
sodium (SODIUM)
potassium (POTAS)
chloride (CHLORIDE)
total protein (T PROT)
albumin (ALBUMIN)
calcium (CALCIUM)
total carbon dioxide (T C02)
total bilirubin (T BILl)
blood urea nitrogen (BUN)
creatinine (CREAT)
glucose (GLUCQSE)
alanine aminotransferase (ALT)
aspartate aminotransferase (AST)
gamma glutamyltransferase (GGT)
alkaline phosphatase (ALK P)
---Gross Necropsy---
Gross necropies were performed on all found dead or moribund sacrificed animals. After 29 days of treatment, all surviving animals were weighed and sacrificed by exsanguination under sodium pentobarbital anaesthesia. Necropsies were performed on all animals by trained personnel using procedures approved by board-certified pathologists. The necropsy included examination of the following, all findings were recorded:
external surfaces
all orifices
cranial cavity
carcass
thoracic, abdominal and pelvic cavities and their viscera
cervical tissues and organs
nasal cavity and paranasal sinuses
external surface of the brain (at necropsy); the external surface of the spinal cord cut surfaces of the brain and spinal cord were examined at the time of tissue trimming.
---Organ Weights---
All animals were weighed prior to necropsy. For each terminally sacrificed animal, the following organs were weighed after careful dissection and trimming to remove fat and other contiguous tissue in a uniform manner:
brain (including brainstem)
spleen
liver
heart
kidneys
thymus*
testes with epididymides
thyroid with parathyroids*
adrenals*
ovaries*
pituitary*
*= Weighed post-fixation.
---Tissue Preservation---
The following tissues from each animal were preserved in 10% neutral buffered formalin:
femoral bone marrow
lung (with mainstem bronchi)
ovaries
lesions
kidneys
adrenals
testes with epididymides
duodenum, jejunum, ileum
thymus
brain with brainstem (medulla/pons, cerebellar cortex, cerebral cortex)
esophagus
pancreas
sciatic nerve w/skeletal muscle
cervical, thoracic and lumbar spinal cord
urinary bladder
pituitary
uterus
thyroid (parathyroids)
heart
liver
spleen
colon, cecum, rectum
stomach
salivary gland (mandibular)
trachea
mesenteric lymph node
Additionally, a femoral bone marrow smear was prepared from all sacrificed animals and preserved in methanol and stained with Wright-Giemsa stain.
---Histopathology---
The aforementioned tissues, except the esophagus, from all control and high-dose animals; and •the heart, liver, kidneys, and gross lesions from all low- and mid-dose animals, were embedded in paraffin, sectioned, stained with haematoxylin and eosin, and examined microscopically. - Other examinations:
- None
- Statistics:
- Mean body weight changes (Weeks 0-4), total food consumption (Weeks 1-4), clinical pathology data (except cell morphology), absolute organ weight and organ-to-body weight ratios of the control group were compared statistically to the data from the same sex of the treated groups.
If variances of untransformed data were heterogeneous, analyses were performed on transformed data to achieve variance homogeneity. When the series of transformations were not successful in achieving variance homogeneity, analyses were performed on rank-transformed data. Group comparisons were performed at 5% two-tailed probability level. - Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- See other information and additional tables.
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- See other information and additional tables.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- See other information and additional tables.
- Food consumption and compound intake (if feeding study):
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Food efficiency:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Water consumption and compound intake (if drinking water study):
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Ophthalmological findings:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Haematological findings:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Clinical biochemistry findings:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Urinalysis findings:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Behaviour (functional findings):
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Immunological findings:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Organ weight findings including organ / body weight ratios:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- See other information and additional tables.
- Neuropathological findings:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Histopathological findings: non-neoplastic:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Histopathological findings: neoplastic:
- not examined
- Description (incidence and severity):
- See other information and additional tables.
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- A NOEL of 300 mg/kg/day of B212.
- Details on results:
- See other information and additional tables.
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 300 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- clinical signs
- other: At 300 mg/kg/day there were insufficient findings to suggest a relationship to treatment.
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Critical effects observed:
- not specified
- Lowest effective dose / conc.:
- 300 mg/kg bw/day (nominal)
- System:
- other: Whole body
- Organ:
- other:
- Treatment related:
- no
- Dose response relationship:
- no
- Relevant for humans:
- not specified
- Conclusions:
- At 300 mg/kg/day B212 there were insufficient findings to suggest a relationship to treatment. On this basis it was concluded that the level represented a no observable effect level for both sexes in this study.
- Executive summary:
The test material, B-212, was administered daily for 29 days to male and female Sprague-Dawley rats by oral gavage in order to evaluate the subchronic toxicity. Corn oil was used as the vehicle. Dose levels were 0, 300, 1500 and 3000 mg/kg/day (Groups 1 through 4, respectively). Criteria evaluated included mortality, cage side and detailed clinical signs, body weight, food consumption, clinical haematology, clinical chemistry, organ weights, organ-to-body weight ratios, gross pathology, and histopathology.
At 3000 mg/kg/day, signs of treatment included death (one male, three females), languid behavior, prostration, hunched, ataxia, and excess salivation. Mean body weight change (Weeks 0-4) was decreased in males compared to control males; the effect was associated with treatment. Other findings included increased alkaline phosphatase (males), total protein (both sexes) and albumin levels (both sexes), and increased liver and kidney weights (absolute and relative, both sexes). Microscopic evaluations revealed minimal centrilobular to diffuse hepatocellar hypertrophy which was accompanied by decreased periportal vacuolization and increased density of hepatocellular cytoplasm. In addition, the kidneys of male rats exhibited increased incidences and severity of protein resorption droplets in the tubular cells. The non-glandular region of the stomach for both sexes exhibited acanthosis, however, the finding was considered of secondary importance compared to other findings.
Animals receiving 1500 mg/kg/day exhibited similar findings (except death) and the incidence and severity of the findings generally followed
At 300 mg/kg/day, the findings were so minimal that it was concluded the level was probably a no effect dosage.
Reference
Mortality. Weekly Clinical and Daily Cageside Observations
Four animals either died or were sacrificed moribund prior to study termination (three high-dose females and one high-dose male). On the basis of findings for the high-dose animals, the deaths were considered treatment-related. However, a diagnosis of the cause of death was not reached.
Isolated incidences of alopecia (paws, legs), salivation, soft faeces, urine stains and sores (mouth) were the only clinical signs noted. None of the signs were considered treatment related.
After two days of dosing one or more of the following daily cage side observations were exhibited in the high-dose animals and in only a few of the mid-dose animals: languid behaviour, prostration, hunched appearance, ataxia, and excessive salivation. These observations were observed for the duration of the study and were considered to be treatment related.
Body Weights and Food Consumption
Statistical analysis of the mean body weight change Weeks 0-4 revealed a significant decrease for the high-dose males when compared to the control. The effect was considered treatment related. Evaluation of the mean total food consumption values revealed no significance differences in either the treated males or females as compared to the control animals.
Clinical Pathology
Evaluation of the haematology data revealed significant increases for bone marrow (myeloid to erythroid ratio) in the mid-dose males, and platelet count in the high-dose males; and significant decreases for the red blood cells and haematocrit of the high-dose females. Evaluation of the clinical chemistry data revealed significant increases in blood urea nitrogen, creatinine, and alkaline phosphatase in the high-dose males; total protein (mid-dose females, and high-dose males and females); total bilirubin (low-dose females) and albumin (mid- and high-dose males and females). Significant decreases were noted for chloride (mid-dose females and high-dose males); glucose (mid-dose females); and total carbon dioxide (high-dose females). Only the alkaline phosphatase, albumin and total protein findings could be ascribed to treatment.
Gross Pathology
In the four high-dose animals that died prior to study termination, gross pathology lesions were noted for the lungs (dark/pale areas and mottled); spleen (pale and small); liver (mottled); kidney (dark/pale areas and pale in appearance); and in the glandular and non-glandular regions of the stomach (dark areas).
In the animals sacrificed at study termination the most frequently noted gross pathology lesion was in the glandular and non-glandular regions of the stomach (thickened, pitted and rough mucosa; prominent vessel and raised areas) of the high-dose animals.
Other incidences were noted throughout the groups but were sporadic and not considered to be treatment related.
Organ Weight Data
A summary of statistically significant findings for the absolute and relative organ weight data is presented below:
Males |
Females |
|||||
Group: |
2 |
3 |
4 |
2 |
3 |
4 |
Dose Level (mg/kg): |
300 |
1500 |
3000 |
300 |
1500 |
3000 |
Terminal Body Weight |
↓ |
|||||
Absolute Kidney |
↑ |
↑ |
↑ |
↑ |
↑ |
|
Relative Kidney |
↑ |
↑ |
↑ |
↑ |
||
Absolute Adrenal |
↑ |
|||||
Relative Adrenal |
↑ |
↑ |
||||
Absolute Liver |
↑ |
↑ |
↑ |
↑ |
||
Relative Liver |
↑ |
↑ |
↑ |
↑ |
||
Absolute Thyroid/parathyroid |
↑ |
|||||
Relative Thyroid/parathyroid |
↑ |
↑ |
||||
Relative Brain w/stem |
↑ |
|||||
Relative Testls/epidid |
↑ |
KEY:↑=Significantly greater than control.
↓=Significantly less than control.
The renal and hepatic organ weight results (Groups 3 and 4) were considered of toxicological significance as they were accompanied by clinical chemistry findings and/or morphological changes. The other organ weight results were not considered to be of toxicological significance.
Histopathology
Hepatic, renal and abdominal effects were produced by B-212 administration. Minimal centrolobular to diffuse hepatocellular hypertrophy which was accompanied by decreased periportal vacuolization and increased density of hepatocellular cytoplasm, increased alkaline phosphatase, increased total protein and albumin levels, and increased liver weights were produced by 3000 mg/kg/day. At 1500 mg/kg/day the hepatic effects were also exhibited in both sexes and were considered to exhibit effects patterns related to dose when compared to the responses at 3000 mg/kg/day. At 300 mg/kg/day, the magnitude of the hepatic effects was very slight and did not evidence a treatment relationship.
Renal findings included increased incidences and severity of protein resorption droplets in the tubular cells of all groups of treated males. The kidney weights (both relative and absolute) were significantly increased and the changes exhibited patterns related to dosage.
The non-glandular region of the stomach in Group 4 animals exhibited acanthosis compared to control animals and the change was considered treatment related.
It was concluded that the primary toxicological findings included the liver and kidney of both sexes of mid- and high-dose animals. In the low-dose animals only the males exhibited renal findings. The abdominal findings were considered, on a comparative basis, to be of secondary importance.
Other sporadic changes observed in the treatment groups were considered consistent with the test species in our laboratory and were not considered treatment related.
DISCUSSION AND CONCLUSION
Three groups of Sprague-Dawley rats received B-212 in corn oil by gavage for 29 days at dose levels of 300, 1500 or 3000 mg/kg/day.
One male and three females, receiving 3000 mg/kg/day, died as a result of treatment during the study. Other signs associated with treatment in this group included languid behavior, prostration, hunched, ataxia and excess salivation. A treatment-related decrease in mean body weight change (Weeks 0-4) was exhibited by the male rats. Clinical and anatomical pathology findings indicated treatment-related changes in the liver and kidney. Alkaline phosphate levels (males), total protein (both sexes) and albumin (both sexes) levels were increased for treated animals compared to controls. The absolute and relative, liver and kidney mean weights were increased for both sexes compared to controls. These findings were accompanied by minimal centrilobular to diffuse hepatocellular hypertrophy, decreased periportal vacuolization and increased density of hepatocellular cytoplasm in the liver. In the kidney, the male rats exhibited increased incidences and severity of protein resorption droplets in the tubular cells.
The non-glandular region of the stomach of the 3000 mg/kg/day animals exhibited acanthosis; the finding was considered treatment-related, but of secondary importance.
Animals receiving 1500 mg/kg/day all survived to termination. Many of the physical signs exhibited by the 3000 mg/kg/day animals were also exhibited in the 1500 mg/kg/day animals. A dose response relationship was noted in results at 1500 mg/kg/day for total protein and albumin values and hepatic and renal histopathology findings. The results indicated this level was the lowest observable effect level for both sexes in this study.
At 300 mg/kg/day B212 there were insufficient findings to suggest a relationship to treatment. On this basis it was concluded that the level represented a no observable effect level for both sexes in this study.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 300 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Three groups of Sprague-Dawley rats received B-212 in corn oil by gavage for 29 days at dose levels of 300, 1500 or 3000 mg/kg/day.
One male and three females, receiving 3000 mg/kg/day, died as a result of treatment during the study. Other signs associated with treatment in this group included languid behavior, prostration, hunched, ataxia and excess salivation. A treatment-related decrease in mean body weight change (Weeks 0-4) was exhibited by the male rats. Clinical and anatomical pathology findings indicated treatment-related changes in the liver and kidney. Alkaline phosphate levels (males), total protein (both sexes) and albumin (both sexes) levels were increased for treated animals compared to controls. The absolute and relative, liver and kidney mean weights were increased for both sexes compared to controls. These findings were accompanied by minimal centrilobular to diffuse hepatocellular hypertrophy, decreased periportal vacuolization and increased density of hepatocellular cytoplasm in the liver. In the kidney, the male rats exhibited increased incidences and severity of protein resorption droplets in the tubular cells.
The non-glandular region of the stomach of the 3000 mg/kg/day animals exhibited acanthosis; the finding was considered treatment-related, but of secondary importance.
Animals receiving 1500 mg/kg/day all survived to termination. Many of the physical signs exhibited by the 3000 mg/kg/day animals were also exhibited in the 1500 mg/kg/day animals. A dose response relationship was noted in results at 1500 mg/kg/day for total protein and albumin values and hepatic and renal histopathology findings. The results indicated this level was the lowest observable effect level for both sexes in this study.
At 300 mg/kg/day B212 there were insufficient findings to suggest a relationship to treatment. On this basis it was concluded that the level represented a no observable effect level for both sexes in this study.
Justification for selection of repeated dose toxicity via oral
route - systemic effects endpoint:
one-generation reproductive toxicity study, performed to recognised
standards and well documented
Justification for classification or non-classification
As the NOAEL of 300 mg/kg/d is well above the CLP guideline concentration values for specific target organ toxicity for repeat dose exposure, the substance can be considered not classified for this endpoint.
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