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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 200-842-0 | CAS number: 75-12-7
- 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
Link to relevant study record(s)
Description of key information
Short description of key information on absorption rate:
Formamide may absorbed via all routes of exposure.
Key value for chemical safety assessment
- Absorption rate - dermal (%):
- 100
Additional information
Physico-chemical properties: data from several independent assessments [cf. section 13: Canada (2009), OECD (2007); ACGIH (2001); GESTIS (2003); MAK (2001)] indicate that formamide is an odourless liquid (melting point 2.55 °C, boiling point 210°C, density 1.334 g/mL at 20°C) that is miscible with water. A slow rate hydrolysis ammonium formate is seen in aqueous solutions. Upon heating to 90°C and above it may decompose and liberate carbon monoxide, ammonia, or hydrogen cyanide. The vapour pressure is low (approx. 8 torre at 25°C), and the vapour saturation concentration is therefore low (0.055 g/m³, or 0.055 mg/L)).
Relevant human routes of exposure: inhalation and dermal contact are considered to represent the most relevant human routes of exposure (ACGIH, 2001; GESTIS, 2003; MAK, 2001; NTP, 2008). It should, however, be kept in mind that the saturation concentration in air is very low, as a result of the low vapour pressure.
Absorption: toxicokinetic and other toxicity studies using rats and mice show that formamide is readily absorbed after inhalation (aerosols), oral and dermal application. Maximum plasma levels are reached within 1 – 2 hours in rats and mice. Toxicokinetic studies indicate presence of a liver first pass effect and complete absorption after oral administration (see Key studies).
Distribution: [14C] formamide distributes uniformly in rats and mice following intraperitoneal or oral administration. Elevated radiolabel concentrations were noted in erythrocytes and in kidneys (Key 3, Key 4)
Elimination: the elimination half-live from plasma is approx. 15 hours in rats and only 4 - 6 hours in mice. In a 90 -day study, plasma levels in rats and mice increased linearly with the oral dose (10, 20, 40, 80, 160 mg/kg bw/day) and also with the increasing time on study. This may reflect accumulation of formamide in repeated dose studies, whereas bio concentration is unlikely to occur (Key 1, Key 2, Supp 1 -4 studies).
Metabolism, excretion:
Approx. 30% of the dose is excreted unchanged in urine within 72 hours, a high fraction is excreted as CO2 (rats about 30%, mice about 50%), and only minor quantities are excreted with the feces (1 – 3%). Approx. 80% of the dose was excreted within 24 hours, and only 3% were found in the carcass after 72 hours. Protein binding increased with time in both species in the order erythrocytes, liver, and muscle. The metabolism depended on the activity of microsomal enzymes, specifically CYP2E1, and in analogy to methylformamide it was proposed that formamide is oxidized to isocyanic acid, which reacts with nucleophils and decomposes in the presence of water to ammonia and CO2 according to the following scheme proposed by key studies 3 and 4):
CYP2E1 CYP2E1
RH-N-CHO ------------------------------------------> RH-N-C=O ----------------------> R-N=C=O [1]
- H . - H .
formamide, R=H isocyanic acid, R=H cyanic acid, R=H
(N-methylformamide, R=CH3 methylisocyanate, R=CH3
decomposition
H-N=C=O + H2O ------------------------------------------------------------------------------> CO2+ NH3 [2]
Though the metabolism of formamide is essentially poorly understood (Supp1 , Supp 4 studies), the above reaction scheme would offer an explanation for the generation of reactive intermediates which can covalently bind to proteins. The formation of carbon monoxide during metabolism was proposed by others but is unlikely. The cleavage of formamide by unspecific amidases to ammonia and formate (GESTIS, 2003) may also occur. This would be in line with the observed carbon dioxide exhalation, but could not explain the observed covalent protein binding.
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.