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EC number: 202-941-4 | CAS number: 101-42-8
- 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

Endpoint summary
Administrative data
Link to relevant study record(s)
Description of key information
A basic toxicokinetics literature search and assessment was performed for the toxicokinetics profile of Fenuron (given below in additional information and as attachment to this record). This includes absorption and distribution, metabolism, excretion and enzyme induction properties. Fenuron is assessed to be well absorbed via both the gastrointestinal and respiratory tract (considered at 100% absorption from conservative viewpoint), whereas dermal absorption is lower (considered at 50% absorption from conservative viewpoint). Fenuron (like urea herbicides) is considered to be metabolised to mono-or di-dealkylated metabolites, which are water soluble and excreted in the urine, therefore bioaccumulation is not likely.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
- Absorption rate - oral (%):
- 100
- Absorption rate - dermal (%):
- 50
- Absorption rate - inhalation (%):
- 100
Additional information
Absorption of Fenuron was assessed as follows based on physicochemical/toxicological data:
- Fenuron is a white odourless solid with mean particle diameter of2.32 µm (respirable). It has a molecular weight of164.2044 g/mol, logP of 0.98, low vapour pressure (0.0021 Pa at 60°C)and is known to be soluble in water (3850 mg/L).
- Based upon the hydrophilic properties, particle size, water solubility and partition coefficient of Fenuron, oral absorption is considered to be likely. This is supported by the oral toxicity findings observed with Fenuron. From a conservative viewpoint, a 100% oral absorption is considered.
- Based on the particle size and partition coefficient of Fenuron, deposition in the deeper airways and absorption by inhalation is possible. As the molecule is water soluble, vapours may already be retained within the mucus of the upper airways. The oral toxicity data indicate that systemic effects are possible, however acute inhalation toxicity testing only showed local but not systemic effects. From a conservative viewpoint, a 100% inhalation absorption is considered.
- Based on low molecular weight of Fenuron with rather high water and low vapour pressure, dermal absorption is possible but limited. When Dermwin is applied, dermal penetration rate seems to be rather low (Kp = 0.000841 cm/hr). From a conservative viewpoint, a 50% dermal absorption is considered.
For the assessment of distribution, metabolism and excretion physicochemical and toxicological properties are taken into account.
- Based upon the low molecular weight and solubility in water, Fenuron is expected to be distributed in the body. This is supported by observed target organs and toxicity (haematological & clinical chemistry findings, increased liver weight).
- From information in literature, urea herbicides are metabolized as follows: mono-or di-dealkylated metabolites are produced by oxidation of alkyl chain of the terminal nitrogen atom.
- Excretion via the urine is expected because Fenuron is soluble in water and metabolites are likely to be present in urine.
- Based on basic toxicokinetics assessment, there are no predilection organs for accumulation, therefore no bioaccumulation is expected.
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