Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 203-474-9 | CAS number: 107-22-2
- 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:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 011
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 011
- Report date:
- 2011
Materials and methods
- Objective of study:
- toxicokinetics
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Version / remarks:
- (1984)
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.7485 (Metabolism and Pharmacokinetics)
- Version / remarks:
- (1998)
- Qualifier:
- according to guideline
- Guideline:
- other: Japan/MAFF Guidelines on the Compiling of Test Results on Toxicity; Tests on In Vivo Fate In Animals (2001)
- GLP compliance:
- yes
Test material
- Reference substance name:
- Glyoxal
- EC Number:
- 203-474-9
- EC Name:
- Glyoxal
- Cas Number:
- 107-22-2
- Molecular formula:
- C2H2O2
- IUPAC Name:
- oxalaldehyde
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: 954-1012
RADIOLABELLING INFORMATION (if applicable)
- Radiochemical purity: 96.1%
- Specific activity: 69.2 MBq/mg
- Locations of the label: 1,2-C14
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: at low temperatures and in the dark
- Solubility and stability of the test substance in the solvent/vehicle:The analytical investigations performed in the context of this study demonstrated the stability, homogeneity and correctness of the concentrations for the period of the test substance administration of 14C-Glyoxal in the vehicle for all performed experiments. - Radiolabelling:
- yes
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Strain as described in the report: Crl:WI(Han)
- Source: Charles River Laboratories, Research Models and Services, Germany GmbH, Sandhofer Weg 7, 97633 Sulzfeld
- Age at start of acclimatization: 6 to 12 weeks
- Weight at study initiation: 250 - 350 g
- Housing: prior test initiation, in groups in Macrolon cages; during experiment, individually in all-glass metabolism cages type Metabowl (Jencons Leighton Buzzard, U.K.) labeled with the project number, animal number, dose and time of first application
- Diet (e.g. ad libitum): Kliba mouse/rat maintenance diet “GLP” (Provimi Kliba SA, Kaiseraugst, Switzerland), ad libitum
- Water (e.g. ad libitum): Tap water, ad libitum
- Acclimation period: planned, duration not specified
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-24
- Humidity (%): 30-70
- Air changes (per hr): air-conditioned room
- Photoperiod (hrs dark / hrs light): 12 h/ 12 h
- Any deviations will be documented
ANALYSIS OF FOOD, WATER, BEDDING
- The food used in the study will be assayed for chemical and microbial contaminants according to the Fed. Reg. Vol. 44, No. 91 of May. 09, 1979, p 27354 (EPA);
- The drinking water is regularly assayed for chemical contaminants both by the municipal authorities of Frankenthal and by the Environmental Analytics Water/Steam Monitoring of BASF SE as well as for bacteria by a contract laboratory. The Drinking Water Regulation will serve as the guideline for maximum tolerable contaminants;
- The bedding (Type Lingocel FS 14 fibres, dustfree bedding, supplied by SSNIFF, Soest, Germany) is regularly assayed for contaminants (chlorinated hydrocarbons and heavy metals). The values given in Lab Animal, Nov.–Dec. 1979, pp 24–33, will serve as the guideline for maximum tolerable contaminants.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
- Radiolabelled and the non-radiolabelled test substance will be prepared in 0.5 % carboxymethylcellulose in tap water.
- For the balance experiments (experiments 4 and 5) and the bile excretion experiments (experiment 8 and 9), the non-radiolabelled test substance will be mixed with the 13C-labelled test substance in a ratio of 1:1 (w:w). In order to achieve the required specific activity, respective amounts of 14C-labelled compound will be added and the mixture will be filled up with 0.5 % carboxymethylcellulose in tap water.
HOMOGENEITY AND STABILITY OF TEST MATERIAL:
The stability, homogeneity and correctness of the concentrations of the test item in the aqueous vehicle will be verified in all experiments by HPLC.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 25 mg/kg bw (total dose)
- Remarks:
- The required quantity of radioactivity per animal was about 0.2-2 MBq. About 10 mL/kg body weight of a preparation will be administered to rats by gavage. Doses were set to 25 and 250 mg/kg bw.
- Dose / conc.:
- 250 mg/kg bw (total dose)
- Remarks:
- The required quantity of radioactivity per animal was about 0.2-2 MBq. About 10 mL/kg body weight of a preparation will be administered to rats by gavage. Doses were set to 25 and 250 mg/kg bw.
- No. of animals per sex per dose / concentration:
- Four males/group
- Control animals:
- no
- Details on study design:
- Following series of nine experiments was conducted with a total of 52 animals.
BLOOD AND PLASMA
Test #1: 4 animals dosed with 250 mg/kg bw, total radioactivity was measured in blood and plasma at different time points;
Test #2: 4 animals dosed with 25 mg/kg bw, total radioactivity was measured in blood and plasma at different time points;
BALANCE AND EXCRETION
Test #3: 4 animals dosed with 250 mg/kg bw, total radioactivity was measured in urine, feces, exhaled air (2 animals), and tissue distribution;
Test # 4: 4 animals dosed with 25 mg/kg bw, total radioactivity was measured in urine, feces, exhaled air (2 animals), and tissue distribution;
Test #5: 4 animals dosed with 250 mg/kg bw of non-labelled test material daily during 14 days, and with 250 mg/kg bw of labelled test material on day 15, total radioactivity was measured in urine, feces, exhaled air (2 animals), and tissue distribution;
TISSUE DISTRIBUTION
Test #6: 12 animals dosed with 250 mg/kg bw, sacrifice of 3 animals/time point at 4 different time points, total radioactivity was measured in different tissues;
Test #7: 12 animals dosed with 25 mg/kg bw, sacrifice of 3 animals/time point at 4 different time points, total radioactivity was measured in different tissues;
EXCRETION VIA BILE
Test #8: 4 animals dosed with 250 mg/kg bw, total radioactivity was measured in excreta and tissue;
Test #9: 4 animals dosed with 25 mg/kg bw, total radioactivity was measured in excreta and tissue. - Details on dosing and sampling:
- COLLECTION OF SAMPLES
Sampling of blood and plasma:
Blood samples (100 – 200 μL) will be taken from the retroorbital sinus under isoflurane anaesthesia at the following time points or by exsanguination (under isoflurane anaesthesia) at the last time point: 1; 2; 4; 8; 24; 48; 72; 96; 120; 144; 168 hours
Sampling of urine, feces and exhaled air:
The dosed animals will be placed in metabolism cages in order to collect urine after 6, 12 and 24 hours and subsequently in time intervals of 24 hours up to 168 hours and feces in intervals of 24 hours up to 168 hours or until 90 % of the applied radioactivity is excreted, whatever occurs first. In the balance experiments 3 and 4, the first two male animals will be placed in closed metabolism cages in order to additionally collect exhaled air for 48 h. If more than 2 % of the total radioactive dose is detected in exhaled air, all experiments will be carried out in closed systems.After 168 hours, animals will be sacrificed and the following tissues will be checked for remaining radioactivity.
Sampling of organs and tissues:
After sacrifice following tissues will be checked for remaining radioactivity: heart, bone, blood cells and plasma, liver, muscle, pancreas, spleen, kidney, thyroid gland, brain, carcass, adrenal glands, skin, adipose tissue, gut and gut contents, lung, testes, stomach and stomach contents, uterus, ovaries, and bone marrow.
Sampling of bile:
Within experiment 8 and 9, the bile duct cannulated and dosed animals will be placed in metabolism cages in order to collect bile in three-hour time intervals.
Cage wash:
For balance estimates the cage wash will also be checked for radioactivity.
RADIOACTIVITY MEASUREMENT
Radioactivity in all samples of biological material will be counted in a liquid scintillation counter. The samples will be prepared for analysis using conventional methods described in standard operating procedures, any additional measures/deviations from standard practice will be detailed in the raw data and the study report. Unless stated otherwise in this protocol or in the study raw data, total radioactivity is measured.
Results and discussion
Main ADME resultsopen allclose all
- Type:
- distribution
- Results:
- highest tissue concentrations were found in the GI tract/GI-tract contents (25 and 250 mg/kg bw)
- Type:
- excretion
- Results:
- 25 mg/kg bw: urine 13.2%, feces 24.3%, and CO2 about 32%
- Type:
- excretion
- Results:
- 250 mg/kg bw: urine 12.2%, feces 27.3%, and CO2 about 30%
- Type:
- other: total recovery of radioactivity
- Results:
- about 110 and 92% of administered doses (25 and 250 mg/kg bw) were recovered
Toxicokinetic / pharmacokinetic studies
- Details on distribution in tissues:
- Following a single oral dose of [14C]-Glyoxal at a dose level of 250 mg/kg bw, tissue distribution was measured 24, 72, 120 and 168 hours post-dosing. At the low dose level of 25 mg/kg bw, the corresponding radioactivity measurements were performed 8, 36, 72 and 144 hours after administration. 24 hours after administration of 250 mg/kg bw [14C]-Glyoxal to male rats highest tissue concentrations (means) were found in the GI tractlGi-tract contents. With the exception of the GI-tract (including its content), highest residues (means) in male rats were found in thyroid, bonemarrow, kidney, liver and adrenal glands and lowest mean radioactive residues at this time point were measured in brain and adipose tissue. In male animals, radioactive residue concentrations generally declined in organs and tissues from the 24 h time point on. The residues in organs and tissues declined slower than the plasma concentration. Nearly no clearance could be observed for skin. Lower clearance than in plasma could be observed e.g. for thyroid and carcass. For other organs and tissues the clearance is observed to be about 50 to 75 % within the observation period. 8 hours after administration of 25 mg/kg bw [14C]-Glyoxal to male rats highest tissue concentrations (means) were found in the GI tract/GI-tract contents. With the exception of the GI-tract (including its content), highest residues (means) in male rats of this dose group were found in thyroid, liver, bonemarrow, pancreas and plasma. Lowest mean radioactive residues at this time point were measured in brain and adipose tissue. In male animals, radioactive residue concentrations declined generally in organs and tissues from the 8 h time point on. The residues in organs and tissues declined slower than the plasma concentration. Nearly no clearance could be observed for skin. For other organs and tissues the decrease in residue levels within the observation period was slower than for plama. Lower clearance than in plasma could be observed e.g. for adipose tissue and carcass.
The tissue distribution experiments showed a correlation between the radioactive residues in organs and tissues and the external dose more or less compareable to the Cmax values of plasma. However, the data indicate a slow partition of the radioactive residues between the compartments of the organism. This may be eventually due to the formation of bound residues in the respective matrices.
- Details on excretion:
- After a single oral administration of 250 mg/kg bw of [14C]-Glyoxal, total recoveries of radioactivity in the balance experiments were > 92 %. In exhaled air, about 30% of the administered radioactivity was excreted as CO2. After 168 hours the total amount of radioactivity excreted in urine was found to be 12.22%. Within 168 hours after single oral administration of 250 mg/kg bw to male rats, 27.30 % of the administered radioactivity were excreted via feces. The time course of the amount of radioactivity found in urine and feces indicates a slow excretion correlating to a residue in carcass after the observation period of one week of up to 30% of the dosed radioactivity. The pattern of excretion after repeated oral administration (14 oral applications with unlabeled Glyoxal at 250 mg/kg bw and one oral application with labeled [14C]-Glyoxal at 250 mg/kg bw) showed higher amounts of radioactivity excreted in urine than in the single dose experiment (21.36 versus 12.22% of dose), lower amounts of excreted radioactivity in feces and higher amounts of exhaled activity but comparable residues in carcass, giving an indication that changes in kinetics 1metabolism occur after multiple dosing of Glyoxal at a dose level of 250 mg/kg. After single oral administration of 25 mg/kg bw the mean total recovery of radioactivity was 109.79% of the administered dose. In exhaled air, about 32% ofthe administered radioactivity was excreted as C02. Within 168 hours after single oral administration of 25 mg/kg bw to male rats, 13.23% of the administered radioactivity were excreted in urine. After 168 hours the total amount of radioactivity excreted via feces was found to be 24.31%. The time course of the amount of radioactivity found in urine and feces indicates a slow excretion correlating to a residue in carcass after the observation period of one week of up to 30% of the dosed radioactivity.
Toxicokinetic parametersopen allclose all
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 1st: 63.5 h
- Test no.:
- #1
- Toxicokinetic parameters:
- Tmax: 24 h
- Test no.:
- #2
- Toxicokinetic parameters:
- half-life 1st: 65.5 h
- Test no.:
- #2
- Toxicokinetic parameters:
- Tmax: 8 h
Metabolite characterisation studies
- Metabolites identified:
- not measured
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.