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1 ments contaminated with PCB 52, PCB 153, and bifenthrin.
2 /PD-L1 inhibitor and pyrethroid insecticide, bifenthrin.
3 ring the clones resistant to the insecticide bifenthrin.
4 versides (Menidia beryllina) were exposed to bifenthrin (1.1 ng/L), cyfluthrin (0.9 ng/L), or cyhalot
5 (98.7%), cis- and trans-permethrin (97.5%), bifenthrin (59.3%), and 3PBA (98.7%) were frequently det
12 ering baseline SCO activity, indicating that bifenthrin amplifies mGluR5 signaling independent of Na(
13 d analogs and absorption of PCB-52, PCB-153, bifenthrin and cis-permethrin were isotropic, validating
14 ons were 27 +/- 3 ng/g and 51 +/- 1 ng/g for bifenthrin and fluxapyroxad transfer experiments, respec
15 samples revealed the presence of pesticides bifenthrin and imazalil at levels below the MRLs establi
16 populations to the commonly used pyrethroid bifenthrin and organophosphate dimethoate were compared
18 gas treatment on the degradation of residual bifenthrin and pirimiphos-methyl insecticides commonly u
19 tein metabolized both type I (permethrin and bifenthrin) and type II (deltamethrin and Lambda-cyhalot
20 4IIEcells, four organochlorine insecticides, bifenthrin, and 3-PBA decreased cortisol-induced PEPCK g
21 urban sediment contamination and identifies bifenthrin as a contaminant of concern in urban wetlands
23 rrelated with both the parent permethrin and bifenthrin concentrations in the tissues of both species
25 by aquatic insect communities and exposed to bifenthrin-contaminated sediment; implications for natur
26 fragmentation behavior of eight pyrethroids (bifenthrin, cyfluthrin, cypermethrin, permethrin, lambda
28 detected in almost half of the samples, with bifenthrin detected the most frequently (41%) and in eac
29 e environmentally relevant concentrations of bifenthrin did not significantly affect the cardiac func
30 e estrogenic samples indicated 2 pesticides (bifenthrin, diuron), 2 alkyphenols (AP), and mixtures of
31 s CYP9Q3 transcripts, whereas the pyrethroid bifenthrin enhances CYP9Q1 and CYP9Q2 transcripts and re
33 n the mesocosm experiment, direct effects of bifenthrin exposure included reduced larval macroinverte
34 solid phase extraction of seven pyrethroids, bifenthrin, fenpropathrin, lambda-cyhalothrin, cyfluthri
35 yos were exposed to 2, 10, 100, and 500 ng/L bifenthrin from fertilization to hatch, and larvae were
36 d larvae were exposed to 2, 10, and 100 ng/L bifenthrin from one day before to 3 days post-hatch.
37 ations (EC50's ranged from 197.6 to 233.5 ng bifenthrin/g organic carbon) previously thought safe for
38 n voltage-gated sodium channels since 100 nM bifenthrin had no effect on the whole-cell Na(+) current
40 from all sites that exceeded the calculated bifenthrin LC50, demonstrating the impact of this contam
42 gical effects of the widely used insecticide bifenthrin on stream ecosystems are largely unknown.
43 the present work was to assess the impact of bifenthrin on the early developmental stages of Longfin
45 In field sediments, the (-)enantiomer of cis-bifenthrin or cis-permethrin was preferentially degraded
46 nmental levels of the estrogenic insecticide bifenthrin or ethinylestradiol (EE2) at 22 degrees C and
47 d a single springtime barrier application of bifenthrin or water according to recommended practices.
48 these data identify a new mechanism by which bifenthrin potently alters Ca(2+) dynamics and Ca(2+)-de
49 lained the experimental time-series data for bifenthrin (R(2) > 0.98) and the remaining unstable pyre
52 osed to wetland sediments was supported by a bifenthrin-spiked sediment experiment, indicating A. sub
54 tudies with permethrin, biotransformation of bifenthrin to estrogenic metabolites was not observed in
55 median lethal effect concentration (LC50) of bifenthrin to laboratory-based A. subtenuis (1.09 (+/-0.
56 redict the bioavailability of permethrin and bifenthrin to two benthic invertebrates (Lumbriculus var
57 ow ng/L) concentrations of ethinylestradiol, bifenthrin, trenbolone, and levonorgestrel from 8 hpf to
58 methyl-6-(phenylethynyl)pyridine] normalized bifenthrin-triggered increase in SCO frequency without a
61 stic concentration of lambda-cyhalothrin and bifenthrin via glass-vial bioassays had these mutations,
63 e significantly correlated with survival and bifenthrin was likely responsible for the majority of th
64 test of delivery, the hydrophobic pesticide bifenthrin was loaded into filomicelles (up to 25% w/w)
66 nd degradation parameters of the insecticide bifenthrin were measured in two soils for (i) the pure a
68 pyrethroid resistance to formulated rates of bifenthrin whereas formulated dimethoate provided optima