ライフサイエンスコーパス: pesticide

1 xtracted (oil yield) and the log Kow of each pesticide.

2 brates and is therefore being developed as a pesticide.

3 ntions aimed at limiting community access to pesticides.

4 l molecules and validated using a set of 131 pesticides.

5 y over-application of conventional synthetic pesticides.

6 ers, 8 PBDE congeners, and 21 organochlorine pesticides.

7 cultural lands and are frequently exposed to pesticides.

8 otency of oxygen analogs of organophosphorus pesticides.

9 in toxicity-weighted use of organophosphate pesticides.

10 targeted interactions between parasites and pesticides.

11 try (UHPLC-MS/MS) for low to medium polarity pesticides.

12 such as the halogenated flame-retardants and pesticides.

13 osure to authorized, unauthorized and banned pesticides.

14 tive identification of suspect and nontarget pesticides.

15 years), sex, and lifetime days of use of any pesticides.

16 were improved and integrated with key modern pesticides.

17 The method was evaluated for 150 pesticides.

18 reusable and reliable analysis of different pesticides.

19 declines, one stressor being the exposure to pesticides.

20 s (ANNs) for the prediction of CCS values of pesticides.

21 pre-exposure alters animals' sensitivity to pesticides.

22 largely focused on national bans of specific pesticides (12 studies of bans in six countries-Jordan,

23 In models evaluating current use of specific pesticides, 19 pesticides were significantly associated

24 or the detection of the two extensively used pesticides, acetamiprid and atrazine.

25 reby benefiting nestmates, many agrochemical pesticides adversely affect bee health even at sublethal

26 microcosms that were either exposed to each pesticide alone, a mix of herbicides, a mix of insectici

27 a simple sample treatment for multi-residue pesticide analysis in milk samples.

28 to produce safety matches, organophosphorous pesticide and phosphor bronze, and the produced N2 might

29 The method was applied to study 80 polar pesticides and >90 transformation products (TPs) in arch

30 We evaluated use of 43 pesticides and 654 lung cancer cases after 10 years of a

31 ted the association of RA with the use of 46 pesticides and across 4 levels (never use and tertiles)

32 We found no interactive effects of pesticides and Bd on anuran survival and no effects of p

33 ent selectivity toward EDI compared to other pesticides and herbicides with similar structures such a

34 ant industrial chemicals used extensively as pesticides and in a variety of therapeutic applications.

35 ported positive associations between several pesticides and lung cancer incidence.

36 ounds with potential use as pharmaceuticals, pesticides and other high-value products.

37 These pesticides and oxygen analogs have previously been ident

38 Monitoring human exposure to pesticides and pesticide residues (PRs) remains crucial

39 proximity to agricultural use of neurotoxic pesticides and poorer neurodevelopment in children.

40 nce of associations between exposure to some pesticides and RA in male farmers.

41 Increased regulation of chemical pesticides and rapid evolution of pesticide resistance h

42 for the simultaneous determination of these pesticides and their metabolites.

43 Our findings further confirm the presence of pesticides and their oxygen analogs in air and highlight

44 or larvae due to genetically modified crops, pesticides, and fertilizers; (b) loss of nectar resource

45 matic hydrocarbons (PAHs), three chlorinated pesticides, and five metals in Norwegian waters and Skag

46 maize and wheat samples were spiked with the pesticides, and they were then stored in the darkness at

47 em mass spectrometry (HILIC-MS/MS) for polar pesticides, and; (iii) reversed-phase liquid chromatogra

48 fluential in the West and Northeast, whereas pesticide application and oil/gas wells correlated with

49 Network (NABO) from 1995 to 2008 with known pesticide application patterns.

50 erage parasite load and its interaction with pesticide application positively predicted malformations

51 lected cumulative monthly samples during the pesticide application seasons and during the winter seas

52 bians, but these effects were strongest when pesticide application was also high, consistent with pri

53 The study sample was drawn from male pesticide applicators enrolled in 1993-1997 who provided

54 a prospective cohort study comprising 57,310 pesticide applicators from Iowa and North Carolina.

55 study.The health consequences of exposure to pesticides are uncertain and subject to much debate.

56 Neonicotinoid pesticides are used in agriculture to reduce damage from

57 sted against a number of other commonly used pesticides as well as in real water samples.

58 members reported lifetime use of 50 specific pesticides at enrollment.

59 0.4-km buffer may not be appropriate for all pesticides because of differing toxicities, fate, and ap

60 containing the average concentration of all pesticide brought into the hive on that particular day,

61 Biological pesticides Bt subsp. Kurstaki is one of the most importa

62 nd most impacted by pollution (nutrients and pesticides), but large annual variability masked any int

63 Pesticides can pose environmental risks, and a common ne

64 reatments on the reduction of some important pesticides (captan, thiamethoxam and metalaxyl) residues

65 The widely used carbamate pesticide carbofuran causes neurophysiological and neuro

66 osed, but actions to end the use of one such pesticide, chlorpyrifos, in agriculture were recently st

67 sure levels of the ollowing organophosphorus pesticides: chlorpyrifos, azinphos-methyl, and their oxy

68 obe was confirmed in the presence of various pesticides, commonly employed in agricultural fields.

69 device is developed for in-situ analysis of pesticide concentration detected via metabolism/photosyn

70 lgal fluorescence is detected to analyze the pesticide concentration in parallel to pH and oxygen sen

71 we found simultaneous exposure to sublethal pesticide concentrations and Bd had no such effect on po

72 Regression analysis indicated that the pesticide concentrations in glacial meltwater and lake w

73 Increased pesticide concentrations in house dust in agricultural a

74 cial melt and streamwater, created pulses in pesticide concentrations in lake water.

75 Polychlorinated biphenyl and organochlorine pesticide concentrations in maternal mid-pregnancy serum

76 lished from 1995 to 2015, we abstracted dust pesticide concentrations reported as summary statistics

77 -regression models of published data on dust pesticide concentrations.

78 idential use exposure pathways to house dust pesticide concentrations: meta-regression of published d

79 Specific pesticides consistently associated with AMD included chl

80 Docking in silico of 121 pesticide contaminants of American hives into the active

81 verall, residues of about 80% of all applied pesticides could be detected with half of these found as

82 and hexachlorobenzene) and three current-use pesticides (dacthal, triallate, and chlorpyrifos) were f

83 now supports the notion that organophosphate pesticides damage the fetal brain and produce cognitive

84 esity with persistent pollutants such as the pesticide DDT and its metabolite p,p'-DDE.

85 e on the association between exposure to the pesticide DDT and its metabolites and obesity to develop

86 Evaluating pesticide degradation and transport in the soil-surface

87 and characterizing a polymeric nanoparticle pesticide delivery vehicle to soybeans, zein nanoparticl

88 tected anthropogenic-organics included eight pesticides (desulfinylfipronil, AMPA, chlorpyrifos, diel

89 a biomimetic biosensor for organophosphorus pesticide detection employing a functionalized polyacryl

90 ing fast, portable, cheap and easy to handle pesticide detection platforms are getting attention of s

91 e some approaches to develop microchip based pesticide detection platforms, there is no compact micro

92 ; therefore, the method could be applied for pesticides determination in routing analysis and custom

93 bled precision detection of organophosphorus pesticides (diazinon(oxon), chlorpyrifos(oxon)) in aqueo

94 mount and distribution of the organochlorine pesticide dichlorodiphenyltrichloroethane (DDT) and its

95 Fruit diameter increases in one millimeter pesticide dissipation rates were reduced in -0.033mgkg(-

96 ions targeting the extreme right tail of the pesticide distribution near human habitation could large

97 sent a model to explore how heterogeneity of pesticide distribution on a comb in the hive can be driv

98 nd larger fields results in increased use of pesticides due to a lack of natural pest control and mor

99 opulation exposed to very high quantities of pesticides (e.g., top 5th percentile, i.e., 4200 kg app

100 As previous studies have reported pesticide effects on bumblebee colony growth, this may s

101 mary explanation for observations of reduced pesticide efficacy over time, but the potential for gene

102 Two historic-use pesticides (endosulfan I and hexachlorobenzene) and thre

103 None of the remaining pesticides evaluated was associated with lung cancer inc

104 Environmental toxicants such as pesticides exert strong selection pressure on many speci

105 ORs for low maternal FA and agricultural pesticide exposure 3 mo before or after conception were

106 Our results suggest that parental pesticide exposure before or during pregnancy may play a

107 birth outcomes associated with agricultural pesticide exposure documented in this study.The health c

108 ally investigate if residential agricultural pesticide exposure during gestation, by trimester, and b

109 why do populations with no known history of pesticide exposure have the ability to induce adaptive r

110 nalyses to estimate odds ratios for maternal pesticide exposure in the month before or during pregnan

111 ll, our analysis indicates that agricultural pesticide exposure increases adverse birth outcomes by 5

112 of the specific mechanisms of non-focal crop pesticide exposure is essential for minimizing risk to b

113 studies reported effects of early sublethal pesticide exposure on amphibian Bd sensitivity and infec

114 Effects of neonicotinoid pesticide exposure on human health: a systematic review.

115 ntification of the relative contributions of pesticide exposure pathways in agricultural populations

116 uring the first pregnancy month and no known pesticide exposure was the reference group for all analy

117 ercial applications to estimate agricultural pesticide exposure.

118 gical study on the health effects of chronic pesticide exposure.

119 link between amphibian sensitivity to Bd and pesticide exposure.

120 utcomes is observed with very high levels of pesticide exposure.

121 this study population, associations between pesticide exposures and ASD were attenuated among those

122 information on maternal supplemental FA and pesticide exposures.

123 Current ecological risk assessment of pesticides fails to protect aquatic biodiversity.

124 Current ecological risk assessment of pesticides fails to protect aquatic ecosystem health.

125 Dissipation curves of all studied pesticides fitted to a first-order decay curve in both t

126 fore studied the effects of a relatively new pesticide, flupyradifurone (FLU), which has been develop

127 be used as an alternative tool to synthetic pesticide for insect pest management in crop production,

128 offer an attractive alternative to chemical pesticides for insect control, and this fungus has been

129 Results showed that pesticide formulations did not affect the initial deposi

130 For this purpose, pesticide-free milled toasted maize and wheat samples we

131 Pesticide-free tea powder spiked at 50 and 100mugL(-1).

132 extend the atmospheric lifetime of reactive pesticides from a few days to weeks, with strong implica

133 We conclude that pesticides from agricultural land use are a major threat

134 es, particularly removal of highly hazardous pesticides from agricultural practice, are likely to be

135 icultural use of five potentially neurotoxic pesticide groups (organophosphates, carbamates, pyrethro

136 Neonicotinoid pesticides have been linked to global declines of benefi

137 (75 antimicrobials, 10 coccidiostats and 121 pesticides) have been selected as relevant compounds.

138 Seven pesticides (herbicides: 2,4-D and simazine; insecticides

139 mass spectrometry (GC-MS/MS) for GC-amenable pesticides; (ii) hydrophilic interaction liquid chromato

140 demonstrated with the identification of the pesticide imazalil, which probably originated from impor

141 l previously untested chemicals, such as the pesticides imazalil and propiconazole.

142 ides," is the most heavily used agricultural pesticide in California and Europe.

143 However, for larvae, clustering of pesticide in the comb can lead to higher exposure levels

144 eholds that had farmed or had used or stored pesticide in the preceding agricultural season were give

145 National bans on commonly ingested pesticides in five of the six countries studied, includi

146 preparation for the multiresidue analysis of pesticides in globe artichoke (Cynara cardunculus L.), a

147 The pesticides in golden and red varieties showed no signifi

148 id analytical method for determination of 89 pesticides in Oolong tea by GC/MS/MS.

149 ue rapidly and efficiently screens, multiple pesticides in Oolong tea.

150 amined combined exposures to maternal FA and pesticides in relation to autism spectrum disorder (ASD)

151 To assess the persistence of pesticides in soil, a multiple-compound screening method

152 icultural land use is a major contributor of pesticides in streams.

153 pathogenic microorganisms, toxic agents, and pesticides in the environmental field and food products

154 o taken into account on the residuals of the pesticides in the samples.

155 n exposure-response relationship for several pesticides including the commonly used herbicides 2,4-D

156 was comprised of 1766104 measurements of 478 pesticides (including metabolites) related to 24743 samp

157 The removal percentage of pesticides increases with increases in ozone concentrati

158 verify that the organic samples were free of pesticides, individual pesticides were analyzed.

159 stigated river delta experiences significant pesticide inputs, leading to environmentally critical co

160 Whether parents used the pesticide inside vs outside the home did not appear to m

161 worldwide ban on the use of highly hazardous pesticides is likely to prevent tens of thousands of dea

162 the current framework for risk assessment of pesticides is not protective against selection for toler

163 ss to pesticides or banning highly hazardous pesticides is one approach to reducing these deaths.

164 organophosphorus chemical warfare agents and pesticides is warranted.

165 Elemental sulfur, "the oldest of all pesticides," is the most heavily used agricultural pesti

166 hod was enlarged to 35 GC and 63 LC amenable pesticides, its overall performance was evaluated and va

167 e this system, we first tested thiram, a DTC pesticide known to display neurotoxic effects, observing

168 ivation involves unregulated applications of pesticides, leading to MRL non-compliances.

169 ention time locked method using a GC-QTOF-MS pesticide library (containing exact mass fragments and r

170 re the extremes of possible heterogeneity of pesticide location/deposition within the hive to compare

171 field-realistic exposure to a neonicotinoid pesticide may seriously compromise this important ecosys

172 n associated with rheumatoid arthritis (RA); pesticides may account for this association, but there a

173 latively little attention has focused on how pesticides may affect Asian honey bees, which provide vi

174 Exposures to specific pesticides may be modifiable risk factors for AMD.

175 This study aimed to evaluate contents of pesticides, metals, sulphites and ochratoxin A in organi

176 The QuPPe (Quick Polar Pesticides) method followed by determination by LC-MS/MS

177 To reflect peak concentrations, current pesticide monitoring needs refinement.

178 ive studies] in homes of farmers who applied pesticides more recently or frequently versus less recen

179 A total of 32 compounds, classified as pesticides, mycotoxins, process-induced toxicants or pac

180 For pesticides, no loss occurred for aldrin, lindane, DDE or

181 sion related to selective toxicity in chiral pesticide, nor on epigenetic changes, such as DNA methyl

182 y account for the frequency with which these pesticides occur as hive contaminants and suggests that

183 orinated biphenyls (PCBs) and organochlorine pesticides (OCPs) are neurodevelopmental toxicants, but

184 orinated biphenyls (PCBs) and organochlorine pesticides (OCPs) were also analyzed for comparison.

185 Likewise, chlorpyrifos, a pesticide often encountered in coral-reefs, impairs A. t

186 social attributes and sub-lethal effects of pesticides on behaviour.

187 Due the negative effects of pesticides on environment and human health, more efficie

188 and Bd on anuran survival and no effects of pesticides on infection load.

189 However, the sublethal effects of pesticides on locomotion and movement to light are relat

190 inhibited by the presence of organophosphate pesticides (OPPs), the subsequent thiocholine-induced ag

191 e irreversibly inhibited by organophosphorus pesticides (OPs), thus, the recovery effect was reduced.

192 with long-term exposure to organophosphorus pesticides (OPs).

193 Regulation aimed at restricting access to pesticides or banning highly hazardous pesticides is one

194 exposure of aquatic ecosystems to individual pesticides or their mixtures can disrupt aquatic microbi

195 regular pregnancy exposure (>/=6 mo) to pet pesticides or to outdoor sprays and foggers were 3.9 (95

196 dy investigated the behavior of semivolatile pesticides over the course of one year and predicted the

197 bility to protect animals from exposure to a pesticide, paraoxon and a warfare agent, VX.

198 rate mass LC-QTOF-MS/MS libraries containing pesticides, pharmaceuticals, and other environmental con

199 ups of drugs as well as contaminants such as pesticides, phenolic compounds and others, are discussed

200 also add to our understanding of the role OC pesticides play in the development of AD.

201 agricultural areas, they may be at risk from pesticide pollution.

202 vels of dieldrin, chlordane- and DDT-related pesticides, polycyclic aromatic hydrocarbons (PAHs), and

203 Organochlorine (OC) pesticides pose a significant environmental risk to wild

204 Maternal supplemental FA and household pesticide product use were retrospectively collected in

205 re but a mixture of insecticides or all five pesticides reduced microbial diversity and altered the c

206 After storage, pesticide removal was higher than 98% for difenoconazole

207 duced water, bleach, VegWash and DI water on pesticide removal.

208 treatment time of EO water resulted in high pesticide removals.

209 trade, there exist scarcely any methods for pesticide residue analysis in these matrices.

210 concluded, EO water can be very effective in pesticide residue removal from fresh produce without aff

211 izing (EO) water treatment on the removal of pesticide residues (diazinon, cyprodinil and phosmet) fr

212 Monitoring human exposure to pesticides and pesticide residues (PRs) remains crucial for informing p

213 dated for screening and quantification of 15 pesticide residues at trace levels in cabbage, broccoli,

214 s in industrial scale in order to remove the pesticide residues from vegetables.

215 edicted focal crop pollen foraging and total pesticide residues, which were dominated by fungicides.

216 f chemical pesticides and rapid evolution of pesticide resistance have increased calls for sustainabl

217 While the resulting development of pesticide resistance in agricultural pest species is wel

218 ution can underlie the emergence of drug and pesticide resistance, cancer, and weeds.

219 Here, we show that pesticide risk in recently accumulated beebread was abov

220 ll as precipitation and seasonal dynamics on pesticide risk taking also concentrations below the limi

221 These results suggest the majority of pesticide risk to honey bees providing pollination servi

222 Furthermore, over 60% of pesticide risk was attributed to pesticides that were no

223 crop pollen foraging was a poor predictor of pesticide risk, which was driven primarily by insecticid

224 Pesticide self-poisoning accounts for 14-20% of suicides

225 641 cases in the control group; incidence of pesticide self-poisoning did not differ between groups (

226 viduals aged 14 years or older, 611 cases of pesticide self-poisoning had occurred by 3 years in the

227 We found no evidence of switching from pesticide self-poisoning to other forms of self-harm, wi

228 kable household containers for prevention of pesticide self-poisoning.

229 improved household pesticide storage reduces pesticide self-poisoning.

230 -poisoning, seem to be effective in reducing pesticide-specific and overall suicide rates.

231 20 457 household pesticide storage containers were distributed.

232 The use of safer household pesticide storage has been promoted to prevent deaths, b

233 t means reduction through improved household pesticide storage reduces pesticide self-poisoning.

234 of olive oil from olives spiked with the 104 pesticides studied, three different chromatographic meth

235 ow cross reactivity with other commonly used pesticides such as fenamiphos, isoproturon, atrazine, li

236 ver, concentrations of levoglucosan and some pesticides such as permethrin peaked during the smolderi

237 We extracted data from studies presenting pesticide suicide data and overall suicide data from bef

238 ical methods, were followed by reductions in pesticide suicides and, in three of these countries, fal

239 s restrictions were followed by decreases in pesticide suicides; one of the two studies investigating

240 had higher indoor air concentrations of both pesticides than did samples from non-farmworker househol

241 Thiamethoxam (TMX) is a common neonicotinoid pesticide that bees can consume in nectar and pollen.

242 The effects of FLU, a pesticide that is reported to be safer than neonicotinoi

243 These results for farmers implicate several pesticides that are commonly used in agricultural and re

244 pyrethrins, which are commercially important pesticides that are strongly toxic to flying insects but

245 over 60% of pesticide risk was attributed to pesticides that were not sprayed during the apple bloom

246 opposed to conventional low molecular weight pesticides, the environmental fate of macromolecular PIP

247 Among women who did not apply pesticides, the husband's use of fonofos was associated

248 Like conventional synthetic pesticides, the use of either Cry protein or dsRNA PIPs

249 ironmental risks, and a common neonicotinoid pesticide, thiamethoxam, decreases homing success in hon

250 ates (DTCs), which are potent fungicides and pesticides, thus raising concern that CS2 may be an envi

251 While the contribution of pesticides to current hive loss rates is debated, remark

252 s used in commerce and the other specific to pesticides, to evaluate which hydrolysis reaction pathwa

253 r results suggest that the ability to induce pesticide tolerance likely arose through evolved antipre

254 We hypothesized that increased pesticide tolerance results from a generalized stressor

255 pecies, many animals might possess inducible pesticide tolerance, buffering them from agrochemical ex

256 including organophosphorous nerve agents and pesticides toward these BChE variants relative to the wi

257 tested for evidence of infectious pathogens, pesticides, toxic metals, and other non-infectious cause

258 sent work was the experimental evaluation of pesticides transfer to virgin olive oil during the produ

259 pathogen treatments (Bd(+), Bd(-)) and four pesticide treatments (control, ethanol vehicle, herbicid

260 Resident behavior such as house tidiness, pesticide usage, and pet ownership showed no significant

261 Information about lifetime pesticide use and other factors was ascertained at enrol

262 nal studies, we found an association between pesticide use and self-reported retinal degeneration.

263 e been linked to numerous factors, including pesticide use and the fungal pathogen Batrachochytrium d

264 have been linked to the effects of increased pesticide use and the spread of disease.

265 Living near pesticide use has been associated with poorer birth outc

266 Occupational pesticide use is associated with lung cancer in some, bu

267 Growing evidence suggests that pesticide use may contribute to respiratory symptoms.

268 and California's comprehensive agricultural Pesticide Use Report data.

269 Data from the California Pesticide Use Reporting System were used to estimate the

270 alifornia has proposed limiting agricultural pesticide use within 0.4 km of schools and childcare fac

271 We estimated agricultural pesticide use within 1 km of maternal residences during

272 tional agriculture but reduces N-surplus and pesticide use.

273 iming related to pregnancy, or applicator of pesticide used influence estimates to an appreciable deg

274 senic loadings to the lake are elevated from pesticides used by early European settlers at a lakeside

275 untreated homes, when the probability that a pesticide was used for the pest treatment was 1-19% and

276 Identification and quantification of 30 pesticides was conducted via high performance liquid chr

277 rs may cause underestimates of the impact of pesticides, we also tested whether this pathway depended

278 samples were free of pesticides, individual pesticides were analyzed.

279 Some specific pesticides were associated with both early- and late-sta

280 llergic wheeze (19 positive, 2 negative); 11 pesticides were associated with both.

281 Pesticides were extracted from the samples by solid phas

282 rent phase I and phase II metabolites of the pesticides were identified in different plant organs suc

283 For the majority of the sites 10-15 pesticides were identified with a detection rate of 45%

284 lorinated biphenyls and eight organochlorine pesticides were investigated.

285 Tests for infectious agents and pesticides were negative.

286 Five detected pesticides were not approved for plant protection use in

287 Pesticides were quantified in air, lake water, glacial m

288 ating current use of specific pesticides, 19 pesticides were significantly associated (p < 0.05) with

289 nsity-weighted lifetime days of use of these pesticides were similar.

290 o consider the fruit growth stage effects on pesticide when performing dissipation studies to define

291 uch as bees can come into contact with these pesticides when foraging in treated areas, with potentia

292 ion promoted the removal of more than 80% of pesticides when the roots were exposed for approximately

293 idue analysis of 189 PCBs, 17 PCDD/Fs and 16 pesticides whereas Cd, As, Pb and Hg were assayed by ICP

294 matrix effects were observed for most of the pesticides which were higher for leaves than fruits.

295 PRETATION: National bans on highly hazardous pesticides, which are commonly ingested in acts of self-

296 bility to environmental contaminants such as pesticides will be dependent on the species, the sensiti

297 ast and complementary detection of different pesticides with algae in a novel glass based microfluidi

298 evaluated the association of currently used pesticides with allergic and non-allergic wheeze among m

299 rgic wheeze (18 positive, 1 negative) and 21 pesticides with non-allergic wheeze (19 positive, 2 nega

300 and tertiles) of lifetime days of use for 16 pesticides with OR>/=1.2 for ever use.