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EC number: 202-805-4 | CAS number: 99-97-8
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- data is from peer reviewed journals
Data source
Reference
- Reference Type:
- publication
- Title:
- Disposition of the test chemical in rats and mice
- Author:
- Dix et.al
- Year:
- 2 007
- Bibliographic source:
- Journal of Toxicology and Environmental Health, Part A: Current Issues, 2007
Materials and methods
- Objective of study:
- excretion
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- The objective of the study was to assess the rates and routes of excretion and tissue distribution of [14C]test chemical-derived radioactivity in F344 rats.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- N,N-dimethyl-p-toluidine
- EC Number:
- 202-805-4
- EC Name:
- N,N-dimethyl-p-toluidine
- Cas Number:
- 99-97-8
- Molecular formula:
- C9H13N
- IUPAC Name:
- N,N,4-trimethylaniline
- Test material form:
- liquid
- Details on test material:
- - Name of test material: Benzenamine, N,N,N-trimethyl-
- Common Name: N,N-Dimethyl-p-toluidine
- Molecular formula: C9H13N
- Molecular weight: 135.209 g/mol
- Smiles notation: c1(N(C)C)ccc(C)cc1
- InChl: 1S/C9H13N/c1-8-4-6-9(7-5-8)10(2)3/h4-7H,1-3H3
- Substance type: Organic
- Physical state: liquid
- Purity: Greater than 99%.
Constituent 1
- Radiolabelling:
- yes
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories; Raleigh, NC
- Age at study initiation: approx 10-12 weeks of age
- Weight at study initiation: Body weight ranges were 180–267 g (male rats), 157–178 g (female rats)
- Housing:From 1 d prior to dosing until sacrifice animals were housed individually in all-glass metabolism cages
- Diet (e.g. ad libitum): Animals were fed Teklad certified rodent diet (W) 8728C (Harlan Teklad, Madison, WI) ad libitum,
- Water (e.g. ad libitum): Muncipal Water supplu, ad libitum
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: Oral dose formulations contained [14C]test chemical and non-radiolabeled test chemical in 10% aqueous Alkamuls EL-620 (Rhodia, Cranbury, NJ). Alkamuls EL-620 (also known as PEG-30 castor oil) was used as an emulsifier. The target dose levels were 2.5, 25, and 250 mg/kg body weight administered in a dose volume of 5 ml/kg for rats. Animals received approximately 5–25 μCi of radioactivity.
DIET PREPARATION
- Rate of preparation of diet (frequency):
- Mixing appropriate amounts with (Type of food):
- Storage temperature of food: - Duration and frequency of treatment / exposure:
- daily
Doses / concentrations
- Remarks:
- 2.5,25,250 mg/kgbw - for male rats
25 mg/kgbw - female rats
- No. of animals per sex per dose / concentration:
- 4 male rats/dose group - 2.5, 25,250 mg/kgbw
4 female rats - 25 mg/kgbw - Control animals:
- not specified
- Positive control reference chemical:
- no data available
- Details on study design:
- no data available
- Details on dosing and sampling:
- TOXICOKINETIC / PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled (delete / add / specify): urine, faeces, blood, plasma, serum or other tissues, cage washes, bile : The following tissues were excised and weighed: samples of blood, adipose, muscle, and skin, as well as the following organs and glands in their entirety: brain, cecum (with contents), heart, kidneys, large intestine (with contents), liver, lung, small intestine (with contents), spleen, stomach (with contents), testes, thyroid, urinary bladder, and uterus. Blood and tissues were solubilized in Soluene- 350, neutralized, bleached as necessary, and analyzed for total radioactivity by LSC. The stomach with contents,
cecum with contents, small and large intestines with contents, tail (iv studies only), and residual carcass were solubilized in ethanolic sodium hydroxide. Weighed aliquots of each digestate were neutralized, bleached, and analyzed for total radioactivity
- Time and frequency of sampling:
- Other: Urine and feces were collected separately from each animal into receptacles cooled on dry ice. Urine was collected at 6, 12, and 24 h; feces were collected at 12 and 24 h. Bladder urine was also collected from the euthanized animals and added to the last urine collection. At the end of each collection interval, the metabolism cages were rinsed with water or ethanol (after the terminal collection only), and the rinsates were analyzed for total 14C content as described for urine. Recovery of radioactivity in the rinsate was added to the recovery of radioactivity in urine at the corresponding time point. Weighed aliquots of urine were analyzed directly for total radioactivity. Aliquots of feces were mixed with an approximately equal mass of water, homogenized, and solubilized in Soluene-350. The solubilized samples were neutralized and decolorized as described earlier before analysis for total radioactivity by LSC. - Statistics:
- Means (reported to three significant figures) and standard deviations are presented. Recovery of radioactivity in a given matrix (i.e., urine, feces, VOCs, 14CO2, and tissues), expressed as percent of administered dose, were analyzed using analysis of variance with the Tukey post test for pairwise multiple comparisons (SigmaStat, version 3.1; Systat Software, Inc., Point Richmond, CA). A p value of <0.05 was considered significant. For male–female comparisons at the mid oral dose within a species, recovery of radioactivity in a given matrix was analyzed using a t-test.
Results and discussion
Main ADME results
- Type:
- excretion
- Results:
- [14C]test chemical-derived radioactivity was rapidly absorbed and excreted at oral doses up to 25 mg/kg. Excretion in urine accounted for approximately 88–94% in rats in the 2.5- and 25-mg/kg dose groups.
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- [14C]test chemical-derived radioactivity was rapidly absorbed and excreted at oral doses up to 25 mg/kg. Excretion in urine accounted for approximately 88–94% in rats in the 2.5- and 25-mg/kg dose groups. The balance of the administered dose was recovered in feces and tissues, with little excreted as exhaled VOCs.
- Details on distribution in tissues:
- For all doses in disposition studies, approximately 1–2% of the administered dose was present in liver 24 h after dosing
- Details on excretion:
- [14C]test chemical-derived radioactivity was rapidly absorbed and excreted at oral doses up to 25 mg/kg. Excretion in urine accounted for approximately 88–94% in rats in the 2.5- and 25-mg/kg dose groups. The balance of the administered dose was recovered in feces and tissues, with little excreted as exhaled VOCs.
Metabolite characterisation studies
- Metabolites identified:
- not specified
Any other information on results incl. tables
At the 250-mg/kg oral dose (aqueous), all rats showed signs of decreased activity, piloerection, blinking eyes, and hunched posture within 10–15 min of dosing.Decreased food and water intake also were observed, but all animals were clinically normal by 24 h.
Applicant's summary and conclusion
- Conclusions:
- At the 250-mg/kg oral dose (aqueous), all rats showed signs of decreased activity, piloerection, blinking eyes, and hunched posture within 10–15 min of dosing.Decreased food and water intake also were observed, but all animals were clinically normal by 24 h.[14C]test chemical-derived radioactivity was rapidly absorbed and excreted at oral doses up to 25 mg/kg. Excretion in urine accounted for approximately 88–94% in rats in the 2.5- and 25-mg/kg dose groups. The balance of the administered dose was recovered in feces and tissues, with little excreted as exhaled VOCs. Recovery of radioactivity in the various matrices, including feces and tissues, was similar for the 2.5-mg/kg dose regardless of route of administration.
- Executive summary:
The objective of the study was to assess the rates and routes of excretion and tissue distribution of [14C]test chemical-derived radioactivity in F344 rats. Oral dose formulations contained [14C]test chemical and non-radiolabeled test chemical in 10% aqueous Alkamuls EL-620 (Rhodia, Cranbury, NJ). Alkamuls EL-620 (also known as PEG-30 castor oil) was used as an emulsifier. The target dose levels were 2.5, 25, and 250 mg/kg body weight administered in a dose volume of 5 ml/kg for rats. Animals received approximately 5–25 μCi of radioactivity. A single oral (2.5, 25, or 250 mg/kg) dose of [14C]DMPT (1–25 mCi) was administered in an aqueous vehicle to male and female Fischer 344 rats. The following tissues were excised and weighed: samples of blood, adipose, muscle, and skin, as well as the following organs and glands in their entirety: brain, cecum (with contents), heart, kidneys, large intestine (with contents), liver, lung, small intestine (with contents), spleen, stomach (with contents), testes, thyroid, urinary bladder, and uterus. Blood and tissues were solubilized in Soluene- 350, neutralized, bleached as necessary, and analyzed for total radioactivity by LSC. The stomach with contents, cecum with contents, small and large intestines with contents, tail (iv studies only), and residual carcass were solubilized in ethanolic sodium hydroxide. Weighed aliquots of each digestate were neutralized, bleached, and analyzed for total radioactivity.Urine and feces were collected separately from each animal into receptacles cooled on dry ice. Urine was collected at 6, 12, and 24 h; feces were collected at 12 and 24 h. Bladder urine was also collected from the euthanized animals and added to the last urine collection. At the end of each collection interval, the metabolism cages were rinsed with water or ethanol (after the terminal collection only), and the rinsates were analyzed for total 14C content as described for urine. Recovery of radioactivity in the rinsate was added to the recovery of radioactivity in urine at the corresponding time point. Weighed aliquots of urine were analyzed directly for total radioactivity. Aliquots of feces were mixed with an approximately equal mass of water, homogenized, and solubilized in Soluene-350. The solubilized samples were neutralized and decolorized as described earlier before analysis for total radioactivity by LSC. At the 250-mg/kg oral dose (aqueous), all rats showed signs of decreased activity, piloerection, blinking eyes, and hunched posture within 10–15 min of dosing.Decreased food and water intake also were observed, but all animals were clinically normal by 24 h.[14C]test chemical-derived radioactivity was rapidly absorbed and excreted at oral doses up to 25 mg/kg. Excretion in urine accounted for approximately 88–94% in rats in the 2.5- and 25-mg/kg dose groups. The balance of the administered dose was recovered in feces and tissues, with little excreted as exhaled VOCs. Recovery of radioactivity in the various matrices, including feces and tissues, was similar for the 2.5-mg/kg dose regardless of route of administration.
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