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EC number: 435-740-7 | CAS number: 94317-64-3
- 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
The object of this study was to assess the the repeat oral dose toxicity and the potential neurotoxicity of the test substance, NBPT, to rats by dietary administration over a period of 13 weeks.
Treatment with NBPT for thirteen weeks at dietary inclusion levels of 0, 200, 1000 and 5000 ppm was associated with a range of effects.
At 5000 ppm, treatment was associated with some reactions that showed subsequent recovery (clinical signs, bodyweight gains, food utilisation, and responses on the functional observational battery) as well as some effects that continued throughout treatment (cumulative food consumption and haematology and biochemistry parameters). Organ weight and histopathological changes were also observed.
At 1000 ppm, there were limited effects on some biochemistry parameters and among females, an increased incidence of luminal dilatation of the uterus.
The no observed effect level (NOEL) was established in the males as being 200 ppm. However, it was not possible to demonstrate a NOEL among females as a slightly lower phosphorus level and a low incidence of luminal dilatation of the uterus was observed. The toxicological significance of these findings, if any, cannot be determined at this time.
Key value for chemical safety assessment
Additional information
- GPT decreased among males in Week 5 and among females in Weeks 5 and 13; GOT decreased among males in Weeks 5 and 13, and among females in Week 5; AP decreased among males in Week 13 and among females in Week 5; phosphorus levels decreased among males in Weeks 5 and 13 and among females in Week 13;
- GOT decreased among males in Week 5; AP decreased among males in Week 13; phosphorus levels decreased among females in Week 13;
- Phosphorus levels decreased among females in Week 13;
Introduction.
The object of this study was to assess the the repeat oral dose toxicity and the potential neurotoxicity of the test substance, NBPT, to rats by dietary administration over a period of 13 weeks.
The neurotoxicity component was designed in accordance with EPA FIFRA Pesticide Assessment Guidelines, SubdivisionF, Addendum 10, Neurotoxicity, published March 1991, which is also applicable to neurotoxicity testing of industrial chemicals for TSCA. Otherwise, this study was designed in accordance with EPA TSCA Test Guidelines, 40 CFR Part 798 - Health Effects Testing Guidelines, September 27 1985, 798.2650, Oral Toxicity and Subsequent Revision, May 20 1987.
The treatment levels employed 0 (control), 200, 1000 and 5000 ppm were selected by the Sponsor based on a two week palatability/toxicity study performed in these laboratories (IMF/6).
The rat was the species of choice due to regulatory requirements and the Crl:CD BR strain was chosen due to availability of background data.
The route of exposure, dietary, was selected since the oral route is a potential route of human exposure to the test material.
Methods.
In this experiment, the toxicity of (N-(n-butyl) thiophosphoric triamide (NBPT), an organophosphorus compound and a urease inhibitor, was assessed in three groups of 15 male and 15 female Crl:CD BR rats which were given NBPT by dietary admixture at levels of 200, 1000 and 5000 ppm for 13 weeks. Dietary inclusion levels remained constant throughout the study. The overall achieved mean intakes in terms of mg/kg/day for main animals were 14.7, 74 and 377 for males and 17.4, 88 and 445 for females. A similar sized group was given untreated diet and acted as controls. Ten animals/sex/group were designated as Main group animals with the remaining five animals/sex/group designated as Satellite animals.
All animals were monitored for clinical signs, bodyweights and food consumption. Water consumption was measured during Week 12. The eyes of all control animals and animals treated at 5000 ppm were subjected to an ophthalmoscopic examination in Week 13. Laboratory investigations (haematology and clinical chemistry) were performed on all Main group animals in Weeks 5 and 13.
During the pre-dose period and Weeks 4, 8 and 13, 5 males and 5 females from the Main group and all the Satellite animals were screened for neurotoxicity (ie scored on a functional observational battery and were quantitatively assessed for locomotor activity). At Week 14 all the Satellite animals were killed using whole body perfusion and selected tissues of the nervous system were then examined histopathologically. At Week 14 all Main group animals were killed, a post mortem examination performed and organ weights were recorded for selected tissues. Histopathology was performed on indicated tissues.
Results.
Clinical signs and mortalities
One female treated at 5000 ppm was considered to be affected by treatment showing signs of unsteady gait, hunched posture and piloerection. These signs were exhibited during Weeks 3 to 10.
There were no mortalities associated with treatment.
Bodyweights
Cumulative gains were statistically significantly lower than controls among males and females treated at 5000 ppm from the commencement of treatment to Week 4. There was a suggestion among males at 5000 ppm of a slight reduction in weight gains during Weeks 8 to 12.
Food consumption
Cumulative intakes (Weeks 1 to 12) among males treated at 5000 ppm were statistically significantly lower than controls.
Efficiency of food utilisation
During the first 3 weeks of treatment, food utilisation was clearly impaired among males and females treated at 5000 ppm.
Water conswnption
There was no effect of treatment.
Neurotoxicity screening
There were transitory changes in behaviour during Week 4 which were characterised by decreased grip strength for all animals treated at 5000 ppm and a low incidence of hunched posture in females at 5000 ppm. With continuing exposure, these changes disappeared.
Ophthalmoscopic examination
There was no effect of treatment.
Haematology
During Week 5, white blood cell counts were statistically significantly lower among males treated at 5000 ppm due to increased lymphocyte counts.
Among females treated at 5000 ppm, platelet counts were statistically significantly increased at Week 5 and Week 13.
Biochemistry
Statistically significant differences were observed in the following parameters at 5000 ppm:
At 1000 ppm the following parameters were statistically significantly different:
At 200 ppm the following parameters were statistically significantly different:
Organ weights
Liver weights when adjusted for bodyweights were statistically significantly increased among males treated at 5000 ppm when compared with controls. Uterus weights of females treated at 1000 or 5000 ppm were statistically significantly increased compared with controls.
Macroscopic pathology
An increased incidence of fluid distension of the uterus was observed among females treated at 200, 1000 or 5000 ppm compared with controls.
Histopathology
Among males, a statistically significantly increased incidence of minimal centrilobular hepatocyte hypertrophy was observed in male rats 5000 ppm. Among female rats, at 5000 ppm, an increase in the incidence of foci of mineralisation in the kidney was observed. There was also a treatment related increase in the incidence of luminal dilatation of the uterus for females treated at all dosages of NBPT.
Neuropathology provided no evidence of neurotoxicity.
Conclusion
Treatment with NBPT for thirteen weeks at dietary inclusion levels of 0, 200, 1000 and 5000 ppm was associated with a range of effects.
At 5000 ppm, treatment was associated with some reactions that showed subsequent recovery (clinical signs, bodyweight gains, food utilisation, and responses on the functional observational battery) as well as some effects that continued throughout treatment (cumulative food consumption and haematology and biochemistry parameters). Organ weight and histopathological changes were also observed.
At 1000 ppm, there were limited effects on some biochemistry parameters and among females, an increased incidence of luminal dilatation of the uterus.
The no observed effect level (NOEL) was established in the males as being 200 ppm. However, it was not possible to demonstrate a NOEL among females as a slightly lower phosphorus level and a low incidence of luminal dilatation of the uterus was observed. The toxicological significance of these findings, if any, cannot be determined at this time.
Justification for classification or non-classification
Treatment with NBPT for thirteen weeks at dietary inclusion levels of 0, 200, 1000 and 5000 ppm was associated with a range of effects.
At 5000 ppm, treatment was associated with some reactions that showed subsequent recovery (clinical signs, bodyweight gains, food utilisation, and responses on the functional observational battery) as well as some effects that continued throughout treatment (cumulative food consumption and haematology and biochemistry parameters). Organ weight and histopathological changes were also observed.
At 1000 ppm, there were limited effects on some biochemistry parameters and among females, an increased incidence of luminal dilatation of the uterus.
The no observed effect level (NOEL) was established in the males as being 200 ppm. However, it was not possible to demonstrate a NOEL among females as a slightly lower phosphorus level and a low incidence of luminal dilatation of the uterus was observed. The toxicological significance of these findings, if any, cannot be determined at this time.
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