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EC number: 617-441-5 | CAS number: 83121-18-0
- 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
Description of key information
Readily biodegradable
A study (BASF DocID: TZ-690-001) was submitted to investigate the ready biodegradability of teflubenzuron under the conditions of OECD 301B. Teflubenzuron is not readily biodegradable according to OECD 301B.
Biodegradation in water and sediment
The DT50 of teflubenzuron was investigated in two water/sediment systems (BASF DocID: 2006/1024568). In water the DT50 ranged between 4.9 and 9.7 days, in total system between 11.4 and 21.4 days. The geomean DT50 of teflubenzuron at 20 °C in freshwater was determined to be 6.9 days. The geomean DT50 in whole system was determined to be 15.6 days at 20 °C.
The geomean DT50 of teflubenzuron was calculated to be 29.6 days at 12 °C in total system and 13.1 days at 12 °C in water (Chapter R.7b, p.222: Endpoint specific guidance Version 4.0 – June 2017).
The following metabolites were formed: 5-chloro-2,4-difluoroaniline (UNK 5 in the DAR, aniline 14C labelled: max 19.04 % AR after 30 d in water phase), 3,5-dichloro-2,4-difluorophenyl-urea (CL-902374, aniline 14C labelled: max 22,45 % AR after 14 d in water phase), 3,5-dichloro-2,4-difluoroaniline (CL-902373, aniline 14C labelled: max 26,42 % AR after 60 d in the sediment phase) and 2,6-difluorobenzoic acid (CL-245508, benzoyl 14C labelled: max 13,79 % AR after 14 d in the water phase).
Biodegradation in soil systems
The Key study Batelle (2003a, 2003/1010910) revealed a DT50 value of teflubenzuron in soil of 181.1 days at 10 °C.
Since for environmental fate modeling soil DegT50 values at reference conditions (temperature of 20°C and soil moisture at field capacity, i.e. pF2) are required, the modeling endpoints (DegT50) reported in Batelle (2003a, 2003/1010910) and Celamerck (1985, TZ-620-004) were normalized following the recommendations of FOCUS [FOCUS (2012): Generic Guidance for Tier 1 FOCUS Ground Water Assessments, version 2.2 (May. 2014), 66 pp.]. The resulting geometrical mean DT50 value was 92.1 days.
- Anaerobic conditions:
Degradation of teflubenzuron under anaerobic conditions was investigated under dark anaerobic conditions in the supporting studies. The RMS considered that the anaerobic experiment performed with the benzoyl labelled substance was not scientifically reliable due to the low recoveries and the potential loss of not trapped volatiles. In the aniline labelled experiment the major metabolite 3,5-dichloro-2,4-difluorophenylurea accounted for a maximum of 28.2 % AR after 14 d under anaerobic conditions. However, anaerobic conditions are not considered to be especially relevant for the representative uses (tomato and apple) evaluated at EU level.
Additional information
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