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1 BAA antagonist (bicuculline or the pesticide dieldrin).
2 e that confers resistance to the insecticide dieldrin.
3 y; however, a suggestive finding emerged for dieldrin.
4 etic mapping of resistance to the cyclodiene dieldrin.
5 e.g., DDT in the western part of Germany and dieldrin.
6 ncrease in basal [Ca(2+)](i) is inhibited by dieldrin.
7 of these two agents than of chlorpyrifos and dieldrin.
8 rgic neuronal degeneration after exposure of dieldrin.
9 ate both receptors, such as clotrimazole and dieldrin.
10  (GABA) receptor subunit gene, Resistance to dieldrin.
11 ing gestation and lactation to low levels of dieldrin (0.3, 1, or 3 mg/kg every 3 days) alters dopami
12 or pendimethalin (1.50; 95% CI: 0.98, 2.31), dieldrin (1.93; 95% CI: 0.70, 5.30), and chlorimuron eth
13 veloped resistance to insecticides including dieldrin, 1,1-bis(p-chlorophenyl)-2,2,2-trichloroethane
14 ns, which were countered by bicuculline (and dieldrin, 5-HT neurons only).
15                                              Dieldrin, a highly persistent organochlorinated pesticid
16      In this paper we describe the effect of dieldrin and a binary mixture of dieldrin and lindane on
17          The combined findings indicate that dieldrin and binary mixtures of organochlorines affect [
18 e effect of dieldrin and a binary mixture of dieldrin and lindane on a critical parameter of neuronal
19    Co-exposure of PC12 cells to a mixture of dieldrin and lindane revealed an additive inhibition of
20       Surprisingly, the effects of diazinon, dieldrin and Ni(2+) showed basic similarities despite th
21 ike, whereas there was strong concordance of dieldrin and Ni(2+) with each other and with each indivi
22 orpyrifos, diazinon) with an organochlorine (dieldrin) and a metal (Ni(2+)) for similarities and diff
23 (chlorpyrifos, diazinon), an organochlorine (dieldrin) and a metal (Ni(2+)) for their effects on neur
24 (chlorpyrifos, diazinon), an organochlorine (dieldrin) and a metal (Ni(2+)); we utilized microarrays
25 polychlorinated biphenyls, DDTs, chlordanes, dieldrin, and alpha- and gamma-hexachlorocyclohexane (HC
26 Gaseous concentrations of hexachlorobenzene, dieldrin, and chlordanes were significantly greater (Man
27 400 and -200 (pg.m(-2).d(-1)) for gamma-HCH, dieldrin, and chlorpyrifos, respectively.
28 ce for an association between pendimethalin, dieldrin, and parathion use and lung cancer risk.
29 id (2,4,5-T); the organochlorine insecticide dieldrin; and the organophosphate insecticides diazinon,
30  The halving times for DDTs, chlordanes, and dieldrin are 8.7 +/- 0.4 years for both the atmosphere a
31 ctures such as diazinon, heptachlor, endrin, dieldrin, butachlor and chlordane.
32 demonstrate that nanomolar concentrations of dieldrin can stimulate microglia to produce ROS that may
33 ropionic acid (2,4,5-TP) and possibly use of dieldrin, captan, and 2,4,5-trichlorophenoxyacetic acid
34                           Elevated levels of dieldrin, chlordane- and DDT-related pesticides, polycyc
35                       Dissolved SigmaHCH and dieldrin concentrations decreased linearly with increasi
36 ors (TN, CN), heptachlor exo-epoxide (HEPX), dieldrin (DIEL), chlorobornanes (SigmaCHBs and toxaphene
37 nazine, picloram, aldicarb, azinphos-methyl, dieldrin, diquat dibromide, endosulfan, and esfenvalerat
38 of two weak environmental estrogens, such as dieldrin, endosulfan, or toxaphene, were 1000 times as p
39  a greater reduction of striatal dopamine in dieldrin-exposed offspring, which was associated with a
40                                Additionally, dieldrin exposure during development potentiated the inc
41 porter 2 (VMAT2) were increased by perinatal dieldrin exposure in a dose-related manner.
42 istone acetylation occurred within 10 min of dieldrin exposure indicating that acetylation is an earl
43  of microglial cells with 0.1 nM to 1 microM dieldrin for 24 h resulted in a concentration-dependent
44  receptors, and overlap between diazinon and dieldrin for the receptors led to a stronger resemblance
45                            The Resistance to Dieldrin gene, Rdl, encodes a GABA-gated chloride channe
46 d by reduced dosage of the Rdl (Resistant to dieldrin), gene encoding a subunit of inhibitory GABA re
47                                     However, dieldrin had more notable effects on neuropeptide recept
48 chlorine (OC) insecticides lindane (HCH) and dieldrin (HEOD) to the development of neurodegenerative
49  dichlorodiphenyltrichloroethane (p,p -DDT), dieldrin, heptachlor epoxide, HCB, trans-nonachlor, oxyc
50              Furthermore, 30-day exposure of dieldrin in mouse models induced histone hyperacetylatio
51 n addition to immortalized microglial cells, dieldrin induced a concentration-dependent ROS generatio
52 n mesencephalic dopaminergic neuronal cells, dieldrin induced a time-dependent increase in the acetyl
53 tment on histone acetylation and its role in dieldrin-induced apoptotic cell death in dopaminergic ne
54 itor anacardic acid significantly attenuated dieldrin-induced histone acetylation, Protein kinase C d
55                             Furthermore, the dieldrin-induced microglial ROS generation was significa
56                                          The dieldrin-induced microglial ROS generation was time-depe
57 mation on the potential role of microglia in dieldrin-induced neurodegeneration in relevance to the d
58       The hyperacetylation was attributed to dieldrin-induced proteasomal dysfunction, resulting in a
59 te that exposure to the neurotoxic pesticide dieldrin induces acetylation of core histones because of
60 n particular, the organochlorine insecticide dieldrin is believed to be associated with PD.
61  data suggest that developmental exposure to dieldrin leads to persistent alterations of the developi
62 ion of the organochlorine pesticides aldrin, dieldrin, lindane, and alpha-endosulfan by using surface
63  Compared with those in the lowest quintile (dieldrin, < 0.57 mug/L), odds of obesity were 3.6 (95% C
64 des (desulfinylfipronil, AMPA, chlorpyrifos, dieldrin, metolachlor, atrazine, CIAT, glyphosate) and t
65 n Vallee du Kou (VK) to pyrethroids, DDT and dieldrin, moderate level for carbamates and full suscept
66 cating that acetylation is an early event in dieldrin neurotoxicity.
67 study, we set out to determine the effect of dieldrin on the production of ROS and the underlying mec
68                        With the exception of dieldrin, our data shows PCBs and other organochlorine p
69 effects on both 5-HT and TH neurons, whereas dieldrin potently inhibited 5-HT neurons only.
70 acid decarboxylase 1 (Gad1) and Resistant to dieldrin (Rdl), genes vital for GABAergic neurotransmiss
71 n of the GABA(A) receptor gene, Resistant to dieldrin (Rdl), in PDF neurons reduces sleep, consistent
72            The GABAA receptor, resistance to dieldrin (Rdl), is highly expressed in the Drosophila mu
73 teracts with the GABAA receptor Resistant to Dieldrin (RDL), upregulating its levels and promoting it
74 le point mutations in the gene Resistance to dieldrin (Rdl), which codes for a subunit of a gamma-ami
75 t from Drosophila melanogaster [Resistant to Dieldrin (RDL)] has been cloned, functionally expressed,
76 rdance between Ni(2+) and either diazinon or dieldrin, reflecting similarities toward the receptors.
77 o includes a biochemical selectable markers, Dieldrin resistance (Dl), on the second chromosome and f
78 s with this duplication exhibit intermediate dieldrin resistance compared with single copy Ser(301) h
79  strong correlation with pyrethroids/DDT and dieldrin resistance.
80                                Surprisingly, dieldrin shared many of the same neuropeptide targets as
81 ic samples; however, some compounds (such as dieldrin) showed reduced concentrations from 7.5-3.4 to
82 ptors is constructed from RDL (resistance to dieldrin) subunits from Drosophila melanogaster.
83  whereas losses exceeding 80% were found for dieldrin, sulfotep or phorate.
84 d among users of the chlorinated insecticide dieldrin, the fumigant mixture carbon-tetrachloride/carb
85 demonstrate that nanomolar concentrations of dieldrin time- and concentration-dependently inhibit dep
86   The most commonly detected pesticides were dieldrin, trans-chlordane, endosulfan I, and chlorpyrifo
87    In this study, we examined the effects of dieldrin treatment on histone acetylation and its role i
88 observed in cells 12-24 h, but not 6 h after dieldrin treatment.
89                                   Aldrin and dieldrin were less potent than endrin in interfering wit
90 nochlorine pesticides, the most abundant was dieldrin, with the highest average concentration of 99 +

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