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EC number: 204-800-2 | CAS number: 126-73-8
- 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
For tributyl phosphate many studies on rats, mice and rabbity are available. The most valid 28 day and 90 day studies in mice and a 2-year study in rats are taken into consideration for assessment. The lowest NOEL of these studies (8.9 mg/kg bw/day), obtained in the 2-year rat study, is taken forward for DNEL derivation.
Key value for chemical safety assessment
- Toxic effect type:
- dose-dependent
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to same study
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: range finding study - low numbers of animals
- Principles of method if other than guideline:
- The study was designed to evaluate the toxicity of tributyl phosphate when administered in the diet to mice for up to 4 weeks and to select dose levels for a 90-day toxicity study and an oncogenicity study to be perfomed with this material.
Tributyl phosphate was administered orally, via dietary admixture, to CD-1 mice (5/sex/group) at initial concentrations of 100, 1000, 5000, and 20000 ppm. However, because total mortality occured at the 20000 ppm level, the lowest dose was escalated from 100 ppm to 10000 ppm of test day 10 in order to provide a suitable range of dose levels. control animals (5/sex/group) received standard laboratory diet. Physical observations and body weight and food consumption measurements were performed on all animals pretest and at selected intervals during the treatment period. After at least 4 weeks of treatment, all survivors were sacrifieced, selected organs were weighed and organ/body and organ/brain weight ratios were calculated. Gross mortem examinations were conducted on all animals. - GLP compliance:
- yes
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Route of administration:
- oral: feed
- Vehicle:
- other: diet
- Analytical verification of doses or concentrations:
- yes
- Duration of treatment / exposure:
- up to 4 weeks
- Frequency of treatment:
- daily (feeding study)
- Remarks:
- Doses / Concentrations:
100, 1000, 5000, 10000, 20000 ppm (100 = 18 (m), 23 (f), 1000 = 165-194 (m), 226-271 (f), 5000 = 765-844 (m), 956-1034 (f), 10000 = 971-1378 (m), 2090-2220, (f)
Basis:
nominal in diet - No. of animals per sex per dose:
- 5/sex/group
- Control animals:
- yes, concurrent vehicle
- Dose descriptor:
- NOEL
- Effect level:
- 1 000 ppm
- Sex:
- male
- Basis for effect level:
- other: 1000 ppm = 165-194 mg/kg/day
- Dose descriptor:
- NOEL
- Effect level:
- 1 000 ppm
- Sex:
- female
- Basis for effect level:
- other: 1000 ppm = 226-271 mg/kg/day
- Dose descriptor:
- LOEL
- Effect level:
- 5 000 ppm
- Sex:
- male
- Basis for effect level:
- other: 5000 ppm = 765-844 mg/kg/day
- Dose descriptor:
- LOEL
- Effect level:
- 5 000 ppm
- Sex:
- female
- Basis for effect level:
- other: 5000 ppm = 956-1034 mg/kg/day
- Critical effects observed:
- not specified
- Executive summary:
The study was designed to evaluate the toxicity of tributyl phosphate when administered in the diet to mice for up to 4 weeks and to select dose levels for a 90-day toxicity study and an oncogenicity study to be perfomed with this material.
Tributyl phosphate was administered orally, via dietary admixture, to CD-1 mice (5/sex/group) at initial concentrations of 100, 1000, 5000, and 20000 ppm. However, because total mortality occured at the 20000 ppm level, the lowest dose was escalated from 100 ppm to 10000 ppm of test day 10 in order to provide a suitable range of dose levels. control animals (5/sex/group) received standard laboratory diet. Physical observations and body weight and food consumption measurements were performed on all animals pretest and at selected intervals during the treatment period. After at least 4 weeks of treatment, all survivors were sacrifieced, selected organs were weighed and organ/body and organ/brain weight ratios were calculated. Gross mortem examinations were conducted on all animals.
Dietary administration of tributyl phosphate to mice for up to 4 weeks produced mortality at a concnetration of 20.000 ppm and signs of toxicity (body weight losses and/or liver weight elevations) at concentrations of 5.000 and 10.000 ppm. Under conditions of this study, the no observed level (NOEL) of tributyl phosphate when administered in the diet to mice was 1.000 ppm (1000 ppm = 165-194 mg/kg/day for males, 226-271 mg/kg/day for females) and the lowest observed effect level (LOEL) was 5.000 ppm.
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EPA OTS 798.2650 (90-Day Oral Toxicity in Rodents)
- Principles of method if other than guideline:
- Tributyl phosphate was administered in the diet to CD-1 mice (15/sex/group at study initiation) at concentrations of 0, 500, 2000, or 8000 ppm for ninety days. Control animals received standard laboratory diet.
- GLP compliance:
- yes
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding labs, Inc., Kingston, New York 12484
- Age at study initiation: 42 days
- Weight at study initiation: males: mean 29.0 g; females: mean 21.3 g
- Housing: individually
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 14 days
DETAILS OF FOOD AND WATER QUALITY:
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-24
- Humidity (%): 36-78 Although the humidity exceeded the desired range on several occasions, it
is believed to have not affected the integrity of this study.
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: July 10, 1990 - Route of administration:
- oral: feed
- Details on route of administration:
- preparation of diet: appropriate amounts of the test material were mixed with Purina Diet '5002 to achieve the desired concentrations. Fresh diet mixes were prepared once weekly.
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- feeding for 7 days per week
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- analyses of test diets were performed by Bio/dynamics.
Homogeneity: Prior to the administration of test diets, mock batches of the low- and high-concentration diets were prepared. Three samples each from the top, middle and bottom portion of the two batches were analyzed (9 samples per concentration; 18 total samples).
Stability: Stability of the test material in the diet for at least two weeks was previously established (Bio/dynamics, Inc., Department of Metabolism and Analytical Chemistry, Study Number
90067). Stability of the test material in the dietary mixture for at least six weeks was determined by performing weekly analyses of the diets prepared for Week 12.
Confirmation of Dietary Concentrations During Study: All dietary levels, for each batch mixed, were assayed (2 samples per concentration). Concentrations within ±15% of the nominal (desired)
concentration were considered acceptable.
Analysis of preliminary batches of diet confirmed that the mixing procedure used produced homogeneous mixtures of tributyl phosphate in the diet. (Stability of diets at room temperature for at least fourteen days after preparation was established in a previous study). Analysis of diets presented to the test animals confirmed that appropriate concentrations were administered. Mean analytical recovery values, expressed as percent of nominal (desired) concentrations, were 100%,
101%, and 102%, for the 500, 2,000, and 8,000 ppm diets, respectively.
Analytical evaluations performed to establish long-term stability of the test material in the diet for future studies confirmed that the test material was stable in the diet for at least six weeks. - Duration of treatment / exposure:
- 3 month
- Frequency of treatment:
- continuous (feeding study)
- Dose / conc.:
- 500 ppm
- Remarks:
- according to 95 mg/kg bw/day for males and 122 mg/kg bw/day for females
- Dose / conc.:
- 2 000 ppm
- Remarks:
- according to 385 mg/kg bw/day for males and 480 mg/kg bw/day for females
- Dose / conc.:
- 8 000 ppm
- Remarks:
- according to 1400 mg/kg bw/day for males and 850 mg/kg bw/day for females
- No. of animals per sex per dose:
- 15/sex/group
- Control animals:
- yes, plain diet
- Details on study design:
- Post-exposure period: no
- Positive control:
- not adequate
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: weekly
BODY WEIGHT: Yes
- Time schedule for examinations: weekly
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes - calculated from food consumption data and based on nominal concentrations
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: Yes / No / Not specified
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: pretest and at termination
- Dose groups that were examined:
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at the 30-day collection via venipuncture of the orbital sinus
- Anaesthetic used for blood collection: Yes (identity) / No / Not specified
- Animals fasted: Yes (3-4 hours prior to blood collection)
- How many animals: 5 per sex/group at the 30-day collection; prior to termination: all survivors
- Parameters checked:
hematocrit
erythrocyte count
reticulocyte count
platelet count
total and differential
leukocyte counts
erythrocyte morphology
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: at the 30-day collection via venipuncture of the orbital sinus
- Animals fasted: Yes (3-4 hours prior to blood collection)
- How many animals: 5 per sex/group at the 30-day collection; prior to termination: all survivors
- Parameters checked:
aspartate aminotransaminase (serum glutamic oxaloacetic transaminase)
alanine aminotransaminase
(serum glutamic pyruvic
transaminase)
creatinine
alkaline phosphatase
albumin
calcium
inorganic phosphorus
PLASMA/SERUM HORMONES/LIPIDS: Yes / No / Not specified
- Time of blood sample collection:
- Animals fasted: Yes / No / Not specified
- How many animals:
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No
- Time schedule for examinations:
- Dose groups that were examined:
- Battery of functions tested: sensory activity / grip strength / motor activity / other:
IMMUNOLOGY: Yes / No / Not specified
- Time schedule for examinations:
- How many animals:
- Dose groups that were examined:
- Parameters checked in table [No.?] were examined.
OTHER: - Sacrifice and pathology:
- Sacrifice: Exsanguination under carbon dioxide anesthesia.
No gross postmortem examinations were performed on animals designated for Month 1 (30-day) Clinical Laboratory Studies (5/sex/dose)
Complete gross postmortem examinations were performed on all animals at study termination (90 days; 10/sex/dose). The terminal necropsy included examination of the external surface and all orifices; the external surfaces of the brain and spinal cord; the organs and tissues of the cranial, thoracic, abdominal, and pelvic cavities and neck; and the remainder of the carcass. In addition, the urinary bladder of each animal was opened and checked for the presence or absence of calculi.
ORGAN WEIGHTS: Yes
adrenals
brain
heart
kidneys
liver (with empty gallbladder)
ovaries
testes (with epididymides)
GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes
The following tissues/organs were examined for all terminally sacrificed animals in the control (Group I) and high-dose (Group IV) groups.
adrenal glands (2)
aorta {thoracic} (1)
hone marrow {sternum} (1)
bone {sternum} (1)
brain {medulla/pons, cerebrum, and cerebellum} (3)
epididymides (2)
esophagus (1)
gallbladder (1)
heart (1)
kidneys (2)
large intestine {cecum, colon, and rectum} (3)
liver {at least 2 lobes} (2)
lungs {with mainstem bronchi} (2)
lymph node {mesenteric} (1)
lymph node {mediastinal} (1)
nerve {sciatic} (1)
ovaries (2)
pancreas (1)
pituitary gland (1)
prostate (1)
salivary gland {mandibular} (1)
small intestine {duodenum, jejunum and ileum} (3)
spinal cord {cervical, mid-thoracic and lumbar} (3)
spleen (1)
stomach (1)
testes (2)
thymus (1)
thyroid glands {with parathyroids} (2)
trachea (1)
urinary bladder (1)
uterus {body/horns with cervix} (2)
gross lesions
The following tissues/organs were examined for all terminally sacrificed animals in the low-dose (Group II) and mid-dose (Group III) groups.
epididymides (2)
kidneys (2)
liver {at least 2 lobes} (2)
lungs {with mainstem bronchi} (2)
testes (2)
urinary bladder (1)
gross lesions and any target organs identified by evaluations of high-dose (Group IV) animals. - Statistics:
- Body weight, change in body weight from Week O (baseline), food consumption, clinical laboratory studies, and organ weights and organ/body and organ/brain weight ratios were analyzed. Mean
values of all dose groups were compared to control values at each time interval.
Statistically significant differences from control values are indicated on mean tables of appendices. - Clinical signs:
- no effects observed
- Description (incidence and severity):
- observations noted were of the type commonly seen in
laboratory mice and/or occurred sporadically throughout the dose groups
and were not related to test material administration. - Mortality:
- no mortality observed
- Description (incidence):
- All animals survived until their scheduled termination dates.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Dietary administration of tributyl phosphate at the highest
concentration (8,000 ppm) resulted in body weight lasses during the first
week of study with subsequent gains. However, mean body weights and/or
mean weight gains for this group were statistically significantly 1ower
than control values for most of the study. Overall, mean body weight
gains for both males and females at the 8,000 ppm level were depressed
with respect to the controls (20% formales and 29% for females). Mean
weight gains of males receiving the 2,000 ppm concentration were slightly
lower than control gains at several intervals; differences were
statistically significant at Weeks 5, 6, 7, 8, 10, and 11. Mean weight
gains for females receiving this concentration were considered comparable
to control values. At 2,000 ppm, overall mean weight gains were
depressed 20% formales and 12% for females. The decreases in body
weight and body weight gain at 8,000 ppm (males and females) and 2,000
ppm (males only) were considered tobe treatment-related. Mean body
weights and weight gains in males and females receiving 500 ppm were
comparable to or higher than concurrent control values. - Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- The only alteration in food consumption values was a statistically
significant decrease, relative to control values, during the initial week
of treatment (Week 1) for animals receiving 8,000 ppm (males and
females). Mean food consumption values for this group were comparable to
control values for the remainder of the study. Food consumption values
for low- and mid-dose groups were considered comparable to control values
throughout the study.
Mean test substance intake (mg/kg/day), calculated on the basis of nominal
dietary concentrations, ranged as follows:
Group II (500 ppm): males 91-102, females 109-135
Group III (2000 ppm): males 355-418, females 429-527
Group IV (8000 ppm): males 1248-1580, females 1514-2020 - Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- no effects observed
- Description (incidence and severity):
- Ophthalmoscopic examinations revealed no indication of test
material related effects. - Haematological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- The only alterations considered suggestive of an effect of
test material administration were slight, statistically
significant, decreases, relative to control values, in the mean
hematocrit and total erythrocyte values for high-dose females at
study termination and a trend toward slightly increased platelet
counts in high-dose males and females at both Month 1 and study
termination. Other hematological parameters showed normal
variability and differences seen were not considered to be related
to dietary administration of tributyl phosphate. - Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Dietary administration of tributyl phosphate at the 8,000 ppm
concentration produced statistically significant elevations in
serum albumin and calcium values for animals, both males and
females, receiving this concentration at both Month 1 and study
termination, with the exception of calcium for females at Month 1.
Serum enzyme levels exhibited a high degree of variability.
However, some differences between the values for control and
treated groups at study termination appeared tobe related to test
material administration. These consisted of statistically
significant elevations, relative to control values, for serum
alanine aminotransferase (ALT) values for high-dose males and
females and alkaline phosphatase values for high-dose males.
Additional differences seen at study termination which were not
statistically significant but which were considered suggestive of
an effect of tributyl phosphate included elevated ALT values for
mid-dose females and elevated serum aspartate aminotransferase
(AST) values for mid- and high-dose females. Two individual high dose
animals (male No. 4004 and female No. 4502) had markedly
elevated AST and ALTlevels at study termination.
In conclusion, some slight hematological alterations and some effects on clinical chemistry parameters of liver function. In the middle concentration slight decrease of weight gains, elevated terminal ALT and AST in females - Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- Dose-related, statistically significant (p >=0.01), elevations,
relative to control values, were evident at study termination in liver
weights, liver/body weight ratios, and liver/brain weight ratios of
animals (both sexes) which received 2,000 or 8,000 ppm of tributyl
phosphate. Absolute and relative liver weights of animals which received
500 ppm were generally comparable to control values.
No effect of test material administration on adrenal, brain, heart,
kidney, ovary, or testes weights was apparent. The few statistically
significant differences which were noted were associated with low
terminal body weight values or appeared to represent normal variability. - Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Grass postmortem examinations revealed alterations in the liver and
microscopic examinations revealed alterations in the liver and urinary
bladder which were considered to represent effects of tributyl phosphate
administration.
Grass enlargement of the liver was evident in all high-dose (8,000
ppm) animals andin one male and one female in the mid-dose (2,000 ppm)
group and brown or tan discoloration of the liver was seen in seven highdose
animals (one male and six females) andin one mid-dose male. - Neuropathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- Microscopically, a dose-related increase in the incidence and severity of
centrilobular hepatocyte hypertrophy was evident in the mid- and highdose
groups. Incidence of this observation are shown in Table 1.
Severity was minimal in control animals, minimal or slight in mid-dose
animals and slight or moderate in high-dose animals.
Microscopic examinations of the urinary bladder revealed the
presence of epithelial hyperplasia in seventeen of the twenty mid-dose
animals (8 males; 9 females) andin all twenty high-dose animals (10
males, 10 females). Severity was minimal or slight in the mid-dose group
and slight or moderate in the high-dose group. The only other
observation of epithelial hyperplasia of the urinary bladder was the
presence of a minimal change in a single low-dose male; this did not
appear tobe toxicologically significant.
0ther lesions observed grossly or microscopically occurred
sporadically or with similar incidences in control and treated groups or
were considered tobe unrelated to test material administration. - Details on results:
- no further information available
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 500 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: liver weight increased, centrilobular hypertrophy of the liver and hyperplasia of the bladder epithelium; 500 ppm = 75 mg/kg bw (according to MAK; about 95 mg/kg bw in males and 122 mg/kg bw in females according to study report)
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 2 000 ppm
- System:
- other: In the middle concentration slight decrease of weight gains, elevated terminal ALT and AST in females and moderately elevated liver weights in both sexes, slight hepatocyte hypertrophy and minimal or slight epithelial hyperplasia of the urinary bladder.
- Organ:
- other: In the middle concentration slight decrease of weight gains, elevated terminal ALT and AST in females and moderately elevated liver weights in both sexes, slight hepatocyte hypertrophy and minimal or slight epithelial hyperplasia of the urinary bladder.
- Treatment related:
- yes
- Dose response relationship:
- yes
- Conclusions:
- No effects of test material administration were evident in animals receiving the lowest concentration (500 ppm = 75 mg/kg bw).
- Executive summary:
In a 90 day study with tributyl phosphate in mice all animals survived, in the highest concentration body weight loss and reduced body gain with reduced food consumption and reduced fecal volume, elevation of absolute and relative liver weights with hepatocyte hypertrophy, slight to moderate epithelial hyperplasia of the urinary bladder, some slight hematological alterations and some effects on clinical chemistry parameters of liver function.
In the middle concentration slight decrease of weight gains, elevated terminal ALT and AST in females and moderately elevated liver weights in both sexes, slight hepatocyte hypertrophy and minimal or slight epithelial hyperplasia of the urinary bladder. No effects of test material administration were evident in animals receiving the lowest concentration (500 ppm). The NOEL was thus determined with 500 ppm, according to 75 mg/kg bw/day.
Referenceopen allclose all
Dose-related, statistically significant elevations, relative to control values, were evident at study termination in liver weights, liver/body weight ratios, and liver/brain weight ratios of animals (both sexes) which received 5.000 or 10.000 ppm of tributyl phosphate. Absolute and relative liver weights of animals which received 1.000 ppm were generally comparable to control values.
No effect of test material administration on brain, kidney or testes weihts was apparent.
Gross postmortem examinations of animals which died at the 20.000 ppm dose level confirmed or were consistent with antemortem observations in these animals. The most commonly-noted findings were the presence of yellow staining of the ano-genital area, emaciation, pallor poor condition, and the presence of black tarry material in the stomach and/or intestines. Examination of animals which received 10.000 ppm of tributyl phosphate revealed gross-evident enlargement of the liver on 4 of 5 females. This is considered with the elevated liver weights which occured in this group. Other gross postmortem findings occured sporadically and were not considered to be related to test material administration. Examination of urinary bladders at terminal necropsy revealed no calculi in any animal.
All animals survived, in the highest concentration body weight loss and reduced body weight gain with reduced food consumption and reduced fecal volume, elevation of absolute and relative liver weights with hepatocyte hypertrophy, slight to moderate epithelial hyperplasia of the urinary bladder, some slight hematological alterations and some effects on clinical chemistry parameters of liver function. In the middle concentration slight decrease of weight gains, elevated terminal ALT and AST in females and moderately elevated liver weights in both sexes, slight hepatocyte
hypertrophy and minimal or slight epithelial hyperplasia of the urinary bladder.
Table 1: Incidence of centrilobular hepatocyte hypertrophy
Group | I | II | III | IV |
Dose (ppm) | 0 | 500 | 2000 | 8000 |
males | 3/10 | 0/10 | 8/10 | 10/10 |
females | 0/10 | 0/10 | 3/10 | 10/10 |
Severity was minimal in control animals, minimal or slight in mid-dose
animals and slight or moderate in high-dose animals.
2000 ppm corresponds to:
MAK: 300 mg/kg bw/day
study report: 385 mg/kg bw/day in males and 480 mg/kg bw/day in females
500 ppm corresponds to:
MAK: 75 mg/kg bw/day
study report: 95 mg/kg bw/day in males and 122 mg/kg bw/day in females
No effects of test material administration was evident in animals receiving the lowest concentration (500 ppm).
NOEL: 75 mg/kg bw/day.
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEL
- 8.9 mg/kg bw/day
- Study duration:
- chronic
- Species:
- rat
- System:
- urinary
- Organ:
- bladder
Additional information
In the 4 week range-finding study tributyl phosphate was administered orally, via dietary admixture, to CD-1 mice (5/sex/group) at initial concentrations of 100, 1000, 5000, and 20000 ppm. Due to total mortality at the 20000 ppm level, the lowest dose was escalated from 100 ppm to 10000 ppm at test day 10 in order to provide a suitable range of dose levels. Control animals (5/sex/group) received standard laboratory diet. In this 4 week study the no observed effect level (NOEL) of tributyl phosphate when administered in the diet to mice was 1.000 ppm (1000 ppm = 165-194 mg/kg/day for males, 226-271 mg/kg/day for females) and the lowest observed effect level (LOEL) was 5.000 ppm.
In the 90-day study tributyl phosphate was administered in the diet to CD-1 mice (15/sex/group at study initiation) at concentrations of 0, 500, 2000, or 8000 ppm for ninety days. Control animals received standard laboratory diet. Physical observations, ophthalmoscopic examinations, body weight and food consumption measurements were performed on all animals pretest and on all surviving animals at selected intervals during the treatment period. Hematology, clinical chemistry, and urinalysis were performed on selected animals at month 1 (day 30) and at study termination. After at least 90 days of treatment, all survivors were sacrificed, selected organs were weighed and organ/body and organ/brain weight ratios calculated. Complete gross mortem examinations and histopathological evaluation of selected tissues were conducted on all terminally sacrificed animals (10/sex/group).
In this 90 day feeding study all animals survived. In the highest concentration body weight loss and reduced body gain with reduced food consumption and reduced fecal volume, elevation of absolute and relative liver weights with hepatocyte hypertrophy, slight to moderate epithelial hyperplasia of the urinary bladder, some slight hematological alterations and some effects on clinical chemistry parameters of liver function. In the middle concentration slight decrease of weight gains, elevated terminal ALT and AST in females and moderately elevated liver weights in both sexes, slight hepatocyte hypertrophy and minimal or slight epithelial hyperplasia of the urinary bladder. No effects of test material administration were evident in animals receiving the lowest concentration (500 ppm). The NOEL was thus determined with 500 ppm, according to 75 mg/kg bw/day.
In a chronic feeding study on SD rats with tributyl phosphate a dose-related increase in the incidence and severity of urinary bladder hyperplasia and the incidence of urinary bladder papillomas was evident in male and female rats receiving the 700 and 3000 ppm concentrations. Based on these effects the no observed effect level (NOEL) for chronic oral administration of tributyl phosphate to rats under conditions of this study was 200 ppm (200 ppm = 8.9 mg/kg bw for males and 11.6 mg/kg bw for females).
The NOEL obtained in this 2-year study is taken forward for DNEL calculation. For details on material, methods, and results of this study please refer to the same study in chapter carcinogenicity.
Justification for classification or non-classification
As stated in the CORAP Substance Evaluation Report of 2021 for tributyl phosphate:
'Considering the evidences overviewed above, the concerns on the possible target organ toxicity for kidneys, spleen and testes are not warranted.' and
'The observed changes in urinary bladder following repeated exposure to tributyl phosphate can be considered as covered appropriately by the Carcinogenic category 2 classification.'
Thus, no classification for repeated dose toxicity is warranted.
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