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EC number: 255-449-7 | CAS number: 41583-09-9
- 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
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:
- comparable to guideline study with acceptable restrictions
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Metabolism, disposition and excretion of 14C-Melamine in male Fischer 344 rats
- Author:
- Mast R.W. et al.
- Year:
- 1 985
- Bibliographic source:
- Food Chem. Toxicol., 21, 807-810, (1983)
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 982
- Report date:
- 1982
Materials and methods
- Objective of study:
- other: metabolism, excretion and disposition
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Deviations:
- yes
- Remarks:
- only one dose level tested
- Principles of method if other than guideline:
- The metabolism, excretion and disposition of melamine were determined after administration of a single oral dose.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Melamine
- EC Number:
- 203-615-4
- EC Name:
- Melamine
- Cas Number:
- 108-78-1
- Molecular formula:
- C3H6N6
- IUPAC Name:
- 1,3,5-triazine-2,4,6-triamine
Constituent 1
- Specific details on test material used for the study:
- RADIOLABELLING INFORMATION
- Radiochemical purity: 98.4 %
- Specific activity: 8.1 mCi/mmol
- Locations of the label: uniformly labelled in the triazine ring - Radiolabelling:
- yes
- Remarks:
- 14 C (uniformly labelled in the triazine ring)
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Kingston, N)
- Weight at study initiation: 250 to 400g
- Fasting period before study: food was withheld for 12 hr before and 4 hr after dosing
12-hr light/dark cycle .
- Housing: singly in glass metabolism chambers for collection of urine, faeces and breath
- Individual metabolism cages: yes
- Diet: ad libitum
- Water: ad libitum
ENVIRONMENTAL CONDITIONS
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- Study design 1 (excretion routes): Intubation with 1 mL of the solution
Study design 2 (tissue distribution and residues): no data (presumably equivalent to study design 1) - Duration and frequency of treatment / exposure:
- Study design 1 (excretion routes): single administration
Study design 2 (tissue distribution and residues): single administration, rats were killed 0.5, 1 .0, 4 .0, 8 .0 . 24, 48 or 96 hr later .
Doses / concentrations
- Dose / conc.:
- 1.3 mg/kg bw (total dose)
- Remarks:
- Study design 1 (excretion routes): 0.025 mCi/rat
Study design 2 (tissue distribution and residues): 0.025 mCi/rat
- No. of animals per sex per dose / concentration:
- Study design 1 (excretion routes): 4
Study design 2 (tissue distribution and residues): 3-4/group - Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
Study design 1 (excretion routes):
- Tissues and body fluids sampled: urine, faeces, and expired air
- Time and frequency of sampling: four consecutive 24hr periods; in one study, expired air was not collected, faeces were collected at 96 hr
and urine at 2, 4, 8, 12, 24, 48, 72 and 96 hr after dosing . The urine from each rat was assayed separately.
Study design 2 (tissue distribution and residues):
- Tissues and body fluids sampled: At autopsy, samples of liver, kidneys, ureters . rinsed bladder and blood were taken and plasma was obtained by centrifugation. The half-life of melamine in the plasma was determined.
MELAMINE DETERMINATIONS
The [14C] in aliquots of plasma, urine and breath-trapping solutions was measured directly by liquid scintillation. [14C] Melamine was measured in urine and in boiling-water extracts of blood, plasma and faeces
Results and discussion
Main ADME resultsopen allclose all
- Type:
- absorption
- Results:
- Tmax= 30 min (blood)
- Type:
- distribution
- Results:
- high level in bladder after 24 h
- Type:
- metabolism
- Results:
- no metabolites detected
- Type:
- excretion
- Results:
- urine major route of elimination (elimination t1/2= 3h)
Toxicokinetic / pharmacokinetic studies
- Details on distribution in tissues:
- Results obtained from study design 2:
Plasma and liver:
The plasma [14C] melamine level 30 min after treatment was 1.1 ppm, but 30 min later, this level had dropped by 53% to 0.52 ppm .
Over the next 3 hr, the plasma [14 C] melamine level dropped by another 52% .
The terminal phase half-life of melamine in plasma was 2.7 hr. Whole-blood and liver levels of [14C] melamine were indistinguishable from plasma levels over this period. At 24 hr or after, no [14C] was detected in the blood or plasma. Melamine levels in liver were 1-2 ppb or less over these periods
Kidney and bladder:
Melamine levels in the kidney were 2-3 times greater than in the plasma. These elevated kidney levels were probably due to renal concentration of the melamine prior to its urinary excretion . At 24 hr or after melamine levels in kidney were 1-2 ppb or less. Bladder radioactivity levels were very high. While bladder levels were similar to the plasma levels 30 min after treatment, they increased to a peak of 6 .6 ppm at 4 hr (26.4 times the plasma level) and showed considerable variability (1 .4, 4 .5 and 14 ppm. At 8 hr the level was still elevated and continued to show marked variability (4.0, 11 and 1 .8 ppm).
This elevated bladder content of [14C] was probably caused by back diffusion or contamination of the tissue by urine. The cause of the high variability between bladders is unknown. At 24 hr or after Melamine levels in the bladder and ureter were higher than those of the other tissues showing the residual effects of the high initial urinary [14C] levels (see also Table 1).
- Details on excretion:
- Results obtained from study design 1:
Urine:
Virtually all the radioactivity was excreted within the first 24 hr and was present in the urine. By 96 hr, 93 ± 4% of the administered radioactivity had been excreted in the urine.
Faeces and breath:
Only 0.20 and 0.64% of the administered radioactivity appeared in breath and faeces, respectively, during the total 96-hr period . The radioactivity in the faeces was most probably the result of urinary contamination. (An additional 4% of the administered radioactivity was recovered in the cage washings . From the urinary data, it seems likely that this 4% was excreted in the first 24 hr . The total recovery of 14C was 99%.
Elimination half-life and renal clearance:
Kinetic analysis of the radioactivity data from urine yielded an elimination half-life of 3.0 hr (95% CI 2 .6-3 .5) and a renal clearance of 2 .5 ± 0 .1 mL/min (mean ± SEM).
Metabolite characterisation studies
- Metabolites identified:
- no
- Details on metabolites:
- While analyzing the samples by HPLC analysis no metabolites could be detected. This is an indication that melamine was not metabolized. Between 97 and 100% of the [14C] in blood and plasma was also present as melamine at all sampling times. Although the percentage of [14C] present as melamine was lower in the faeces, the total non-melamine [14C] in faeces accounted for less than 0.14% of the administered radioactivity (see also Table 2).
Any other information on results incl. tables
Table I . Concentrations of [14C]melamine in the tissues of male Fischer 344 rats treated orally with a single dose of 0.025 mCi
Melamine concentration (ppb) in: |
|||||||
Time after treatment (hr) |
No of rats |
Blood* |
Plasma |
Bladder |
Liver |
Kidney |
Ureter |
0.5 |
Similar to plasma levels |
1.1 |
Similar to plasma levels |
Similar to plasma levels |
No data |
||
1.0 |
“ |
0.52 |
No data |
“ |
|||
4.0 |
“ |
0.25 |
6.6 (high variability) |
“ |
|||
8.0 |
No data |
||||||
24.0 |
3 |
0 |
ND |
31 +/- 15 |
1.8 +/- 0.1 |
1.3 +/- 0.7 |
12 +/- 4 |
48.0 |
3 |
0 |
0 |
4 +/- 2 |
2.6 +/- 1.2 |
0.7 +/- 0.9 |
9 +/- 5 |
96.0 |
4 |
0 |
0 |
8 +/- 2 |
0.4 +/- 0.2 |
0.1 |
12 +/- 5 |
* Limit of detection 1ppb
Data are expressed as means +/- SEM for the numbers of rats indicated
Table 2: Percentage of radioactivity present as melamine in the urine, blood, plasma and faeces
14C as 14C-melamine* (% of total) in: |
||||
Time after treatment (hr) |
Urine |
Blood |
Plasma |
Faeces |
0.5 |
98.9+/- 6.2 |
98.5+/- 0.4 |
||
1.0 |
99.3+/- 0.1 |
99.4+/- 0.1 |
||
4.0 |
99.5+/- 0.1 |
99.1+/- 0.1 |
||
8.0 |
97.4+/- 1.9 |
98.3+/- 0.8 |
||
24.0 |
98.5+/- 0.1 |
78.4 +/- 2.9 |
||
48.0 |
98.1+/- 0.2 |
64.2 +/- 2.8 |
||
72.0 |
94.9+/- 2.2 |
|||
96.0 |
96.5+/- 0.8 |
* *Radiochemical purity of [14C]melamine in dosing solution was 98 %.
Values are means ± SEM for groups of three or four rats .
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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