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EC number: 253-575-7 | CAS number: 37640-57-6
- 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

Specific investigations: other studies
Administrative data
- Endpoint:
- nephrotoxicity
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Limited description of experimental details.
Data source
Reference
- Reference Type:
- publication
- Title:
- Determination of Spatial Distribution of Melamine-Cyanuric Acid Crystals in Rat Kidney Tissue by Histology and Imaging Matrix-Assisted Laser Desorption/Ionization Quadrupole Time-of-Flight Mass Spectrometry
- Author:
- Kim CW, Yun J-W, Bae I-H, Lee J-S, Kang H-J, Joo K-M, Jeong H-J, Chung J-H, Park Y-H,† and Lim K-M
- Year:
- 2 010
- Bibliographic source:
- Chem. Res. Toxicol. 2010, 23, 220–227
Materials and methods
- Principles of method if other than guideline:
- Spatial distribution of melamine cyanurate crystals in kidney after 3-day feed application
- GLP compliance:
- no
- Type of method:
- in vivo
- Endpoint addressed:
- repeated dose toxicity: oral
Test material
- Details on test material:
- obtained from Sigma- Aldrich (St. Louis, MO, USA).
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- age: 5-6 months old
body weight: 250-270 g
Supplier: Orientbio, Seoul, Korea
The animals were housed in polyethylene cages in an environment with a controlled temperature of 24 ( 2 °C, a constant humidity of 50 ( 10%, and a 12 h light-dark cycle. Animals had free access to a standard diet from Purina Korea and tap water ad libitum. The rats were acclimatized for at least 1 week prior to the experiment and were randomly assigned into different groups.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Remarks:
- 1% in water
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 3 days
- Frequency of treatment:
- once daily
- Post exposure period:
- none
Doses / concentrations
- Remarks:
- Doses / Concentrations:
25 (12,5 M + 12,5 C), 50 (25 M+25C) and 100 (50 M + 50 C) mg/kg bw
Basis:
actual ingested
- No. of animals per sex per dose:
- 6
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Thirty minutes before the administration of M+CA, blood samples were collected from the retro-orbital plexus into a vacutainer serum-separating tube (BD Diagnostic, Sparks, MD) for clinical biochemistry using a Selectr E automated analyzer (Vital Scientific, Dieren, Netherlands). For urine collection, rats of the control group and 100 mg/kg/day M+CA-treated group were placed in metabolism cages after the final dose, and urine samples were collected over a 24 h period.
Urine samples were evaluated for creatinine and specific gravity was analyzed with refractometer (ATAGO, Japan). Rats were anesthetized by isoflurane inhalation 24 h after the last dose, and terminal blood samples were obtained from the inferior vena cava for clinical chemistry. Kidneys were removed, weighed, and preserved in 10% neutral-buffered formalin for histopathology.
Examinations
- Examinations:
- Histopathology of kidneys
Clinical signs
Changes in body weight
Changes in food consumption
BUN
Urea
Creatinine clearance - Positive control:
- no
Results and discussion
- Details on results:
- Visual counting of crystalline deposits shows that rats exposed to a middle dose, 50 mg/kg M+CA, produced renal crystals mainly in the medullar region, while at a high dose, 100 mg/kg M+CA, crystals appeared diffusely throughout the renal cortex and medulla, indicating that M+CA crystals were formed along the osmotic gradient of the kidney. Only the animals with crystals in their kidneys showed increased BUN and creatinine.
Rats given a low dose of 25 mg/kg/day M+CA (12.5 melamine/12.5 cyanuric acid) did not show any evidence of renal impairment or kidney toxicity upon clinical pathologic and histopathologic examination.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

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