ライフサイエンスコーパス: insecticide

1 affordable products (diagnostics, drugs and insecticides).

2 economic losses and increased application of insecticide.

3 esticide risk, which was driven primarily by insecticides.

4 ary exposure (e.g., via leaves) for systemic insecticides.

5 entalis on plants that were not treated with insecticides.

6 target-site of pyrethroid and organochlorine insecticides.

7 nce appreciable exposures to a wide range of insecticides.

8 des and binary mixtures of cyanobacteria and insecticides.

9 of resistance development to a wide range of insecticides.

10 were showing significant resistance to these insecticides.

11 to preserve the effectiveness of pyrethroid insecticides.

12 tly less susceptible than T. tabaci to these insecticides.

13 on mosquitoes to develop resistance to these insecticides.

14 a mix of insecticides, or a mix of all five insecticides.

15 the pervasive use of systemic neonicotinoid insecticides.

16 llinator exposure to neonicotinoid and other insecticides.

17 l background for rational development of new insecticides.

18 have been ascribed in part to neonicotinoid insecticides.

19 ocesses they are major targets for effective insecticides.

20 era, has developed strong resistance to many insecticides.

21 , it is also possible to apply nonpyrethroid insecticides.

22 sites, which could be potential targets for insecticides.

23 , respectively type I and type II pyrethroid insecticides.

24 n of mating disruption and use of biological insecticides.

25 by allowing resistant insects to metabolize insecticides.

26 gnostics and production of steroid drugs and insecticides.

27 ferential susceptibilities of the species to insecticides.

28 ls and strategies to restore the efficacy of insecticides.

29 highest exceedances found for neonicotinoid insecticides.

30 ganophosphate, pyrethroid, and neonicotinoid insecticides.

31 The PRs included 16 fungicides (52%), 8 insecticides (26%), 2 herbicides (6%), 3 pesticide deriv

32 8), benzimidazoles (20), coccidiostats (14), insecticides (3), dyes (12) and others (3).

33 n the setting of indoor residual spraying of insecticide, adding monthly DP to daily TMP-SMX did not

34 vector population and in turn protecting the insecticide against the spread of insecticide resistance

35 s a powerful tool for developing tailor-made insecticides against new target insects.

36 cide, propiconazole (the synergist), and the insecticide, alpha-cypermethrin, on the mortality of the

37 Resistance to an insecticide always spreads slower if that insecticide is

38 the major component of spinosad, an organic insecticide and an FDA-approved agent used worldwide.

39 After administration of insecticide and fungus, activities of glutathione-S-tran

40 ntinuous presence of agricultural chemicals (insecticides and a fungicide) over the last 40 years.

41 ere, provide valuable starting points toward insecticides and are complementary to existing and new c

42 posure to different cyanobacteria, different insecticides and binary mixtures of cyanobacteria and in

43 ion of organophosphorous chemicals including insecticides and chemical warfare agents.

44 ement has relied on multiple applications of insecticides and cultural practices such as removal of w

45 012 to characterize prenatal exposure to IRS insecticides and exposures' impacts on child health and

46 lepidopteran insecticides, non-lepidopteran insecticides and fungicides.

47 r bond found in a variety of organophosphate insecticides and nerve agents.

48 chemicals and suggests a possible role of OC insecticides and PCBs in the etiology of metastatic pros

49 organophosphate [OR=2.0 (95% CI: 1.3, 3.0)] insecticides and phenoxyacetate herbicides [OR=1.9 (95%

50 was carried out on the dissipation of three insecticides and three fungicides during the freezing of

51 t of new methods of prevention (vaccines and insecticides) and treatment (single dose drugs) of the d

52 m to encounter high or low concentrations of insecticide, and allows selection pressures and dominanc

53 henyl)ethane (DDT), the first organochlorine insecticide, and pyrethroid insecticides are sodium chan

54 low-up, 39% of the women reported ever using insecticides, and 1,081 were diagnosed with breast cance

55 onitoring systems, threshold-based selective insecticides, and biological control.

56 s that could potentially reduce or eliminate insecticide application for control of Lygus and the ass

57 agement of mosquito-associated diseases, and insecticide application is the most important component

58 the importance of external factors, such as insecticide applications, in mediating the outcome of in

59 Systemic neonicotinoid insecticides are increasingly used as a crop protection

60 Several pyrethroid and neonicotinoid insecticides are most effective for controlling the inse

61 miologic and laboratory studies suggest that insecticides are related to increased breast cancer risk

62 t organochlorine insecticide, and pyrethroid insecticides are sodium channel agonists.

63 Pesticide insecticides are used on wheat grains in storage units b

64 door-resting mosquitoes, such as bednets and insecticides, are currently the cornerstone of malaria c

65 on's Silent Spring, pesticides, particularly insecticides, arguably remain the most influential pest

66 as restricted the use of three neonicotinoid insecticides as seed dressings on bee-attractive crops.

67 Here, we used fipronil, a broad-spectrum insecticide, as a model chemical to probe its enantiosel

68 to strong selection with glucose-containing insecticide baits.

69 technology that is compatible with existing insecticide-based control methods.

70 Insecticide-based interventions have contributed to appr

71 s detected here as increasing selection from insecticide-based interventions may change the dynamic i

72 s to the future to highlight some of the new insecticide-based tools under development and the challe

73 en largely attributable to the deployment of insecticide-based vector control tools such as bed nets

74 Traditional insecticide-based vector-control programmes have limited

75 direct ecological effects of the widely used insecticide bifenthrin on stream ecosystems are largely

76 ed to environmental levels of the estrogenic insecticide bifenthrin or ethinylestradiol (EE2) at 22 d

77 Sorption and degradation parameters of the insecticide bifenthrin were measured in two soils for (i

78 In H4IIEcells, four organochlorine insecticides, bifenthrin, and 3-PBA decreased cortisol-i

79 glyphosate herbicides, chemical lepidopteran insecticides, biological lepidopteran insecticides, non-

80 Individual insecticides but not herbicides reduced the microbial di

81 They are used in commercial formulations of insecticides, but are also frequently used in the elucid

82 Neonicotinoids are widely used insecticides, but their use is subject of debate because

83 Multiple pest resistances to these insecticides by the 1990s, and increasing consumer deman

84 the microbial diversity and richness and two insecticides, carbaryl and permethrin, also altered the

85 pesticides (herbicides: 2,4-D and simazine; insecticides: carbaryl, dimethoate, disulfoton, and zeta

86 shoppers with simultaneous doses of both the insecticide chlorantraniliprole and the fungal pathogen,

87 rethroids could improve the efficacy of this insecticide class and overcome resistance in field popul

88 eased the efficacy of the most commonly used insecticide class of pyrethroids.

89 Resistance to pyrethroids, the sole insecticide class recommended for treating bed nets, thr

90 he current status of resistance to the major insecticide classes in African malaria vectors, consider

91 Honeybees were most sensitive to insecticides (clothianidin > dimethoate >> tau-fluvalina

92 studies have focused on three neonicotinoid insecticides (clothianidin, imidacloprid, and thiamethox

93 of residual bifenthrin and pirimiphos-methyl insecticides commonly used in storage wheat grains, as w

94 The contact insecticide DDT has been reappraised as a safe, life-sav

95 unds and contrasted resistance levels to the insecticide deltamethrin.

96 le, a mixture may last 5 years while the two insecticides deployed individually may last 3 and 4 year

97 ene expression variation at loci involved in insecticide detoxification.

98 rget sites and target-specific compounds for insecticide development.

99 identifying channel blockers of interest to insecticide discovery or biosecurity.

100 If insecticides do not reliably kill homozygous sensitive g

101 istant malaria vectors following exposure to insecticides does not diminish the threat of growing res

102 Mixtures are favoured when insecticide effectiveness (their ability to kill homozyg

103 interactively impact individual fitness and insecticide efficacy.

104 to differ depending on the concentration of insecticide encountered.

105 malaria control, its use contributes to high insecticide exposure in sprayed communities and raises c

106 We found no impact of insecticide exposure on colony weight gain, or the numbe

107 In total, insecticide exposure was predicted to reduce the lifetim

108 should not discount mosquitoes that survive insecticide exposure with fewer than six legs, as they m

109 tance and elevate the detrimental effects of insecticide exposure, demonstrating how environmental co

110 the relationship, if any, between individual insecticide exposures and breast cancer risk.

111 mental concentrations (PEC) for 466 cases of insecticide field concentrations measured in European su

112 Topical application of an acetone insecticide formulation to circumvent lipid-based uptake

113 New topical insecticide formulations have proven to be effective in

114 pyrethroid resistance, IRS using alternative insecticide formulations may be needed to achieve substa

115 (IMD) is the most widely used neonicotinoid insecticide found on environmental surfaces and in water

116 tness relative to susceptible populations in insecticide free environments.

117 The older generation of insecticide groups has been largely replaced by a pletho

118 of Uganda where indoor residual spraying of insecticide had recently been implemented.

119 cline in the armament of registered chemical insecticides has stimulated research into environmentall

120 cultural use of diazinon, an organophosphate insecticide, has raised serious environmental health con

121 ingredients in residential and agricultural insecticides have changed over time, due in part to regu

122 rees treated with one of three neonicotinoid insecticides (imidacloprid, thiacloprid, or acetamiprid)

123 ally used as a model organism to investigate insecticide impacts on bees, but relatively little is kn

124 aying (IRS) with a pyrethroid (deltamethrin) insecticide in the first year and a carbamate (bendiocar

125 the first year and a carbamate (bendiocarb) insecticide in the two subsequent years.

126 are the most frequently and largely applied insecticide in the world due to their biodegradable natu

127 In adjusted models, concentrations of insecticides in carpet dust decreased for three of four

128 potential determinants of concentrations of insecticides in carpet dust, such as home and garden use

129 channel is the primary target for pyrethroid insecticides in insect pests.

130 We measured concentrations of insecticides in one carpet-dust sample from each of 434

131 n and quantification of (five) neonicotinoid insecticides in sugarcane juice.

132 These experiments demonstrated that insecticide-induced leg loss had no significant effect u

133 idespread and intensive use of neonicotinoid insecticides induces negative cascading effects on ecosy

134 ral landscape is most beneficial to reducing insecticide inputs; reality is far more complex.

135 nets (LLINs) and indoor residual spraying of insecticide (IRS) are the primary vector control interve

136 men protected by indoor residual spraying of insecticide (IRS).

137 an insecticide always spreads slower if that insecticide is used in a mixture although this may be in

138 Defining the molecular targets of insecticides is crucial for assessing their selectivity

139 proportion of mosquitoes that encounter the insecticide) is low.

140 changes in active ingredients have impacted insecticide levels measured in homes.

141 herbicides (atrazine, glyphosate), and three insecticides (malathion, carbaryl, permethrin) on microb

142 gene families for chemoreception, toxin and insecticide metabolism, cuticle proteins, opsins, and aq

143 nutafailed to grow using the organophosphate insecticide methyl parathion as sole source of phosphate

144 The use of chemical lepidopteran insecticides might be associated with hepatic dysfunctio

145 rol, ethanol vehicle, herbicide mixture, and insecticide mixture) for 14 d to quantify survival and i

146 Radical oxidation of carbamate insecticides, namely carbaryl and carbofuran, was invest

147 s in carpet dust decreased for three of four insecticides no longer sold for residential use: chlorda

148 pteran insecticides, biological lepidopteran insecticides, non-lepidopteran insecticides and fungicid

149 mine the combined benefit (forage) and cost (insecticide) of oilseed rape grown from thiamethoxam-tre

150 and delayed (>24 h after exposure) impact of insecticides on daily survival and malaria transmission

151 bial diversity or structure but a mixture of insecticides or all five pesticides reduced microbial di

152 oci (e.g. the Ace-1 target site of carbamate insecticides) or detoxification genes has been implicate

153 sticide alone, a mix of herbicides, a mix of insecticides, or a mix of all five insecticides.

154 of herbivore densities by aerial spraying of insecticide over 20 hectares.

155 Although ever use of insecticides overall was not associated with breast canc

156 ding to pNP production from hydrolysis of an insecticide, paraoxon, in a coupled assay involving phos

157 rcentage change in the concentration of each insecticide per year, adjusting for significant determin

158 of stressors (e.g., either cyanobacteria or insecticides) performed better than general models devel

159 ly used herbicides 2,4-D and glyphosate, the insecticides permethrin and carbaryl, and the rodenticid

160 interplay between evolutionary adaptation to insecticide pressure and variable environmental conditio

161 , imidacloprid, acetamiprid and thiacloprid) insecticides previously extracted from fruit and vegetab

162 s was dominated by intensive organophosphate insecticide regimes to control tortricid leafrollers.

163 All samples had very low amounts of insecticide residues (37 compounds), cyanide, and trypsi

164 etermined nutrients, chemical contaminants, (insecticide residues and heavy metals), and natural toxi

165 osquitoes is threatened by the appearance of insecticide resistance and therefore new control chemica

166 flexible, two-locus model for the spread of insecticide resistance applicable to mosquito species th

167 P450 monooxygenases play a critical role in insecticide resistance by allowing resistant insects to

168 Synergists can counteract metabolic insecticide resistance by inhibiting detoxification enzy

169 Insecticide resistance can arise from a variety of mecha

170 Insecticide resistance has decreased the efficacy of the

171 Fitness-related costs of evolving insecticide resistance have been reported in a number of

172 Insecticide resistance in malaria vectors could presage

173 is study investigated the molecular basis of insecticide resistance in Malaysian populations of Ae. a

174 The role of cuticle changes in insecticide resistance in the major malaria vector Anoph

175 elling strategy to investigate the spread of insecticide resistance in vector populations and demonst

176 Insecticide resistance is a growing threat to mosquito c

177 Insecticide resistance is a major obstacle to control of

178 nagement enables potato production, although insecticide resistance is becoming an issue.

179 Understanding the molecular basis of insecticide resistance is key to improve the surveillanc

180 Insecticide resistance is typically associated with alte

181 burden and the continued spread of drug and insecticide resistance make malaria elimination both via

182 The implications of insecticide resistance management of B. tabaci on Indian

183 A major impediment to the implementation of insecticide resistance management strategies is that evi

184 An understanding of insecticide resistance mechanisms would help to develop

185 ed our understanding of the genetic basis of insecticide resistance over the last decade, we still kn

186 f the environmental background in developing insecticide resistance phenotypes, and caution for the i

187 Insecticide resistance poses a significant and increasin

188 Insecticide resistance threatens the success achieved th

189 However, increasing drug and insecticide resistance threatens the successes made with

190 improve efficacy, an urgent need as emerging insecticide resistance threatens their future.

191 udy is a summary of the current level of the insecticide resistance to selected organophosphates, pyr

192 However, the emergence of insecticide resistance within mosquito vectors risks jeo

193 ndation for future research on mechanisms of insecticide resistance, human-bed bug and symbiont-bed b

194 tigating the possible association of CN with insecticide resistance, three assays were compared for t

195 ersal, extreme polyphagy, and development of insecticide resistance, together with human activities,

196 germanica L.) populations, which differed in insecticide resistance, with either nutritionally rich o

197 tegies most likely to minimise the spread of insecticide resistance.

198 ation of association between the Vgsc CN and insecticide resistance.

199 y undermines vector control programs through insecticide resistance.

200 d LLIN effectiveness in the presence of high insecticide resistance.

201 iont interactions, and several mechanisms of insecticide resistance.

202 ave important implications for the spread of insecticide resistance.

203 ecting the insecticide against the spread of insecticide resistance.

204 nsporters have previously been implicated in insecticide resistance.

205 ravel and commerce in addition to widespread insecticide resistance.

206 ya vector, is threatened by growing cases of insecticide resistance.

207 entation of new technologies that circumvent insecticide resistance.

208 The emergence of insecticide resistant insect pests is of significant con

209 Insecticide resistant populations of insects often have

210 d by drug-resistant Plasmodium parasites and insecticide-resistant Anopheles mosquitoes, and first ge

211 efficacy of Metarhizium against wild-caught, insecticide-resistant anophelines.

212 loping new classes of insecticides to combat insecticide-resistant mosquitoes and the transmission of

213 -regulation of AMPs in experimental lines of insecticide-resistant P. xylostella.

214 e lifetime malaria transmission potential of insecticide-resistant vectors by two-thirds, with delaye

215 ed to be 2 and 5microgkg(-1) for the studied insecticides, respectively, with the exception of imidac

216 nagement programs largely depend on chemical insecticides, resulting in high economic and environment

217 osts associated with resistance suggest that insecticide rotation or utilization of non-insecticidal

218 mosquitoes that enter treated properties the insecticide selects for vector phenotypes deflected by t

219 phosphates and hence that the usage of these insecticides should be reconsidered.

220 s for the women's and husbands' use of these insecticides showed limited concordance.

221 Analytes included four insecticides sold for indoor home use during our study p

222 Concentrations of other insecticides sold for indoor use (carbaryl, cypermethrin

223 Neonicotinoid insecticides specifically have been detected in surface

224 yme SpnF involved in the biosynthesis of the insecticide spinosyn A in Saccharopolyspora spinosa is t

225 95% CI 0.04-0.96, p=0.045), as did residual insecticide spraying of household walls (0.52, 0.31-0.87

226 ol policy in India restricts use of residual insecticide sprays to domestic dwellings.

227 Weight is a strong predictor of insecticide susceptibility and bigger mosquitoes are mor

228 for the interpretation of data generated by insecticide susceptibility assays.

229 ions in larval rearing conditions change the insecticide susceptibility phenotype of adult Anopheles

230 Insecticide susceptibility to 4% DDT and 0.05% deltameth

231 adult female mosquitoes from representative insecticide-susceptible and -resistant strains of An. ga

232 One population was an insecticide-susceptible laboratory strain; the other two

233 ant species, while in plots not treated with insecticides, T. tabaci remained the predominant species

234 sistent levels of resistance to fipronil, an insecticide targeting on gamma-aminobytyric acid (GABA)

235 ls of contamination in pollen are pyrethroid insecticides targeting mosquitoes and other nuisance pes

236 In turn, insecticides targeting this pathway suppress vitellogene

237 nformation for development of sodium channel insecticides that target key insect pests without harmin

238 difficulty in combating thrips vectors with insecticides, the best way to limit/prevent tospovirus-i

239 r their sensitivity toward the neonicotinoid insecticide thiacloprid using their feeding rate as resp

240 periment with pulsed contaminations with the insecticide thiacloprid.

241 chemical sensors for detection of two common insecticides - thiamethoxam and imidacloprid.

242 The capacity of mosquitoes to resist insecticides threatens the control of diseases such as d

243 ical scaffolds for developing new classes of insecticides to combat insecticide-resistant mosquitoes

244 Pyrethroids remain one of the most used insecticides to control Aedes mosquitoes, despite the de

245 Malaria control is reliant on insecticides to control the mosquito vector.

246 s, there is no strong evidence linking these insecticides to losses of the majority of wild bee speci

247 ctin and beta-cypermethrin are commonly used insecticides to manage thrips in China, and laboratory b

248 exposure during the registration of systemic insecticides to safeguard ecosystem integrity.

249 o evaluate the contribution of neonicotinoid insecticides to worldwide pollinator declines have focus

250 arriers, to the formulation of cosmetics and insecticides, to the fabrication of nanostructured mater

251 ity, we observed an up to 8-fold increase in insecticide tolerance in a total of 17 macroinvertebrate

252 trials in which both species were exposed to insecticide treated cabbage plants, F. occidentalis beca

253 malaria control via funding for long-lasting insecticide treated nets (LLINs), indoor residual sprayi

254 Current control tools such as insecticide treated nets or indoor residual sprays targe

255 (>10 per 10,000) and low coverage (<50%) of insecticide-treated bed nets and antimalarial drugs incl

256 , 2 years after distribution of long-lasting insecticide-treated bed nets, the prevalence of malaria

257 361 (72%) were women, and 442 (88%) reported insecticide-treated bednet use.

258 for diarrhoea, pneumonia, and malaria (23%), insecticide-treated bednets (20%), vaccines (17%), reduc

259 Insecticide-treated bednets (ITNs) are effective in prev

260 Mass drug administration and distribution of insecticide-treated bednets timed to coincide with the 2

261 onutrients) and other health products (e.g., insecticide-treated bednets, soap, and water disinfectan

262 ldren aged 0-5 y, adjusting for age, gender, insecticide-treated net (ITN) use, indoor residual spray

263 Kenya and linked it to data on residence and insecticide-treated net (ITN) use.

264 r markers of drug resistance, and to measure insecticide-treated net (ITN) use.

265 cation; OR 1.31, 1.22-1.41), had a household insecticide-treated net (ITN; vs no ITN; OR 1.21, 1.13-1

266 nce survey data, with case management rates, insecticide-treated net usage, and drug campaign coverag

267 This association was not modified by insecticide-treated net use or gravidity, and remained s

268 tween gestation weeks 12 and 28 and given an insecticide-treated net.

269 protected pregnancies (i.e., those not using insecticide-treated nets [ITNs]) leading to live births

270 Long-lasting insecticide-treated nets are generally the most cost-eff

271 Population coverage of insecticide-treated nets increased by 8.34 percentage po

272 trimethoprim-sulfamethoxazole (TMP-SMX) and insecticide-treated nets remain the main interventions f

273 th larviciding, distribution of long-lasting insecticide-treated nets, indoor residual spraying, and

274 bigger mosquitoes are more likely to survive insecticide treatment.

275 ls, the species co-existed on cabbage before insecticide treatments began, but with T. tabaci being t

276 retinoblastoma was associated with parental insecticide use (odds ratio [OR], 2.8; confidence interv

277 We examined associations between insecticide use and breast cancer incidence among wives

278 his substantially eliminated organophosphate insecticide use by 2001, replacing it with pest monitori

279 Here, we use data on crop production and insecticide use from over 100,000 field-level observatio

280 sity, field size, and cropland extent affect insecticide use in practice.

281 Further, we find insecticide use increases with increasing field size.

282 grated pest management the myriad effects of insecticide use on arthropod pest species.

283 onents of landscape simplification influence insecticide use over space and for different crops.

284 relation to the women's and their husbands' insecticide use using Cox proportional hazards regressio

285 find that higher crop diversity does reduce insecticide use, but the relationship is strongly influe

286 mers and their wives provided information on insecticide use, demographics, and reproductive history

287 e-dependent, with nearby cropland decreasing insecticide use, whereas cropland further away increases

288 use, whereas cropland further away increases insecticide use.

289 insect-resistant crops significantly reduces insecticide use.

290 and contributed to major reductions in total insecticide use.

291 ing the relative merits of sequential use of insecticides versus their deployment as a mixture to min

292 Use of several organophosphate insecticides was associated with elevated breast cancer

293 ive ingredients (herbicides, fungicides, and insecticides); we then selected fludioxonil, a halogenat

294 nomic losses and an increased application of insecticide, which eventually may compromise the future

295 Despite intensive research efforts, new insecticides will not reach the market for at least 5 ye

296 new repellents by combining a high-toxicity insecticide with a candidate repellent initially effecti

297 ro-2,2-bis(4-chlorophenyl)ethane), a contact insecticide with a rich and controversial history since

298 sent viable molecular targets for developing insecticides with new mechanisms of action.

299 s long been dominated by the use of chemical insecticides, with the aim of instantaneously killing en

300 hroids are now the fourth most used group of insecticides worldwide.