NOMENCLATURE
Common name chlorfénapyr ((
m) F-ISO); chlorfenapyr (BSI, E-ISO, ANSI)
IUPAC name 4-bromo-2-(4-chlorophenyl)-1-ethoxymethyl-5-trifluoromethylpyrrole-3-carbonitrile
Chemical Abstracts name 4-bromo-2-(4-chlorophenyl)-1-(ethoxymethyl)-5-(trifluoromethyl)-1
H-pyrrole-3-carbonitrile
CAS RN [122453–73–0] Smiles code CCOCn1c(c(C#N)c(Br)c1C(F)(F)F)c2ccc(Cl)cc2
PHYSICAL CHEMISTRY
Mol. wt. 407.6
M.f. C
15H
11BrClF
3N
2O
Form White solid.
M.p. 101–102 °C
V.p. <1.2 × 10
-2 mPa (20 °C)
Kow logP = 4.83
S.g./density 0.355 (24 °C)
Solubility In water 0.14 mg/l (
pH 7, 25 °C). In hexane 0.89, methanol 7.09, acetonitrile 68.4, toluene 75.4, acetone 114, dichloromethane 141 (all in g/100 ml, 25 °C). (
EPA Fact Sheet).
Stability In air,
DT50 0.88 d (10.6 h, calc.). In water (direct photodegradation), DT
50 4.8–7.5 d. Stable to hydrolysis (pH 4, 7 and 9).
APPLICATIONS
Biochemistry Oxidative removal
in vivo of the
N-ethoxymethyl group generates the active species, which is a mitochondrial uncoupler.
Mode of action Insecticide and acaricide with mainly stomach and some contact action. Exhibits good translaminar, but limited systemic, activity in plants.
Uses Control of many species of insects and mites, including those resistant to carbamate, organophosphate and pyrethroid
insecticides and also chitin-synthesis inhibitors, in cotton, vegetables, citrus, top fruit, vines and soya beans. Among pests resistant to conventional products which are controlled by chlorfenapyr are
Brevipalpus phoenicis (leprosis mite),
Leptinotarsa decemlineata (Colorado potato beetle),
Helicoverpa spp.,
Heliothis spp.,
Plutella xylostella (diamond-back moth) and
Tetranychus spp. Also control of many species of structural and household
Formicidae (especially
Camponotus,
Iridomyrmex,
Monomorium and
Solenopsis spp.),
Blattellidae (especially
Blatta,
Blattella,
Periplaneta and
Supella spp.),
Kalotermitidae (especially
Incisitermes spp.) and
Rhinotermitidae (especially
Reticulitermes,
Coptotermes and
Heterotermes spp.), at use rates of between 0.125% and 0.50%
a.i. w/w.
Phytotoxicity No phytotoxicity observed at field use rates.
ANALYSIS
Product by glc.
Residues by hplc. Details from BASF.
ENVIRONMENTAL FATE
Animals In rats, >60% of orally administered chlorfenapyr was excreted, primarily through faeces, within 24 hours. The absorbed residues were metabolised via
N-dealkylation, dehalogenation, hydroxylation and conjugation. Parent and less polar metabolites were found in egg, milk and tissues such as fat and liver. Metabolism in hens and goats is similar to that in rats, however, in these species, 80% of orally administered chlorfenapyr was rapidly excreted. Unexcreted residues were present in kidney and liver. At the potential maximum dietary burden, all residues are <0.01 ppm. Chlorfenapyr is the only significant residue component.
Plants In cotton, citrus, tomato, lettuce and potato, chlorfenapyr is dealkylated to the insecticidally active component (AC 303268) or debrominated to less toxic metabolites. Chlorfenapyr does not translocate out of treated plant parts. Parent compound is the prominent residue.
Soil/Environment In soil, chlorfenapyr is the major residue. Debromination to a less toxic metabolite is the primary route of degradation; dealkylation is not a primary route of degradation in soil.
Koc >10 000 ml/g, indicating chlorfenapyr is likely to be strongly bound in soils. In water,
DT50 (direct photodegradation) 4.8–7.5 d; stable to hydrolysis at pH 4, 7 and 9.
ECOTOXICOLOGY
Birds Acute oral
LD50 for mallard ducks 10, bobwhite quail 34 mg/kg.
LC50 (8 d) for mallard ducks 9.4, bobwhite quail 132
ppm.
Fish LC50 (48 h) for carp 500 μg/l. LC
50 (96 h) for rainbow trout 7.44, bluegill sunfish 11.6 μ;g/l.
Daphnia LC50 (96 h) 6.11 μg/l.
Algae EC50 for
Selenastrum capricornutum 132
ppb.
Bees LD50 0.2 μg/bee.
Worms NOEC (14 d) for
Eisenia foetida 8.4 mg/kg.