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1 ments contaminated with PCB 52, PCB 153, and bifenthrin.
2 (98.7%), cis- and trans-permethrin (97.5%), bifenthrin (59.3%), and 3PBA (98.7%) were frequently det
5 ering baseline SCO activity, indicating that bifenthrin amplifies mGluR5 signaling independent of Na(
6 d analogs and absorption of PCB-52, PCB-153, bifenthrin and cis-permethrin were isotropic, validating
7 samples revealed the presence of pesticides bifenthrin and imazalil at levels below the MRLs establi
9 gas treatment on the degradation of residual bifenthrin and pirimiphos-methyl insecticides commonly u
10 tein metabolized both type I (permethrin and bifenthrin) and type II (deltamethrin and Lambda-cyhalot
11 4IIEcells, four organochlorine insecticides, bifenthrin, and 3-PBA decreased cortisol-induced PEPCK g
12 urban sediment contamination and identifies bifenthrin as a contaminant of concern in urban wetlands
14 rrelated with both the parent permethrin and bifenthrin concentrations in the tissues of both species
16 by aquatic insect communities and exposed to bifenthrin-contaminated sediment; implications for natur
17 fragmentation behavior of eight pyrethroids (bifenthrin, cyfluthrin, cypermethrin, permethrin, lambda
19 detected in almost half of the samples, with bifenthrin detected the most frequently (41%) and in eac
20 e estrogenic samples indicated 2 pesticides (bifenthrin, diuron), 2 alkyphenols (AP), and mixtures of
21 s CYP9Q3 transcripts, whereas the pyrethroid bifenthrin enhances CYP9Q1 and CYP9Q2 transcripts and re
23 n the mesocosm experiment, direct effects of bifenthrin exposure included reduced larval macroinverte
24 ations (EC50's ranged from 197.6 to 233.5 ng bifenthrin/g organic carbon) previously thought safe for
25 n voltage-gated sodium channels since 100 nM bifenthrin had no effect on the whole-cell Na(+) current
27 from all sites that exceeded the calculated bifenthrin LC50, demonstrating the impact of this contam
29 gical effects of the widely used insecticide bifenthrin on stream ecosystems are largely unknown.
31 In field sediments, the (-)enantiomer of cis-bifenthrin or cis-permethrin was preferentially degraded
32 nmental levels of the estrogenic insecticide bifenthrin or ethinylestradiol (EE2) at 22 degrees C and
33 d a single springtime barrier application of bifenthrin or water according to recommended practices.
34 these data identify a new mechanism by which bifenthrin potently alters Ca(2+) dynamics and Ca(2+)-de
35 lained the experimental time-series data for bifenthrin (R(2) > 0.98) and the remaining unstable pyre
38 osed to wetland sediments was supported by a bifenthrin-spiked sediment experiment, indicating A. sub
40 tudies with permethrin, biotransformation of bifenthrin to estrogenic metabolites was not observed in
41 median lethal effect concentration (LC50) of bifenthrin to laboratory-based A. subtenuis (1.09 (+/-0.
42 redict the bioavailability of permethrin and bifenthrin to two benthic invertebrates (Lumbriculus var
43 methyl-6-(phenylethynyl)pyridine] normalized bifenthrin-triggered increase in SCO frequency without a
47 e significantly correlated with survival and bifenthrin was likely responsible for the majority of th
48 test of delivery, the hydrophobic pesticide bifenthrin was loaded into filomicelles (up to 25% w/w)
50 nd degradation parameters of the insecticide bifenthrin were measured in two soils for (i) the pure a
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