ライフサイエンスコーパス: pesticide

1 pollutants, metals, phthalates, phenols, and pesticides).

2 ional nitroenamine [(R(1)N)(R(2)N)C=CHNO(2)] pesticide.

3 nse of cucumber plants exposed to nanocopper pesticide.

4 t climate change factor on the toxicity of a pesticide.

5 group and the proportion of suicides due to pesticides.

6 Organophosphates (OPs) are used worldwide as pesticides.

7 th a high burden of suicides attributable to pesticides.

8 ergic blockers, antivirals, antibiotics, and pesticides.

9 iquid-liquid micro-extraction techniques for pesticides.

10 t surface strongly affect more water-soluble pesticides.

11 ch can be related to changes caused by field pesticides.

12 o its use in plastics, textiles, paints, and pesticides.

13 to evaluate RCC risk in relation to various pesticides.

14 tus of some crops can be leveraged to reduce pesticides.

15 studies have investigated links to specific pesticides.

16 r accessibility and good sensitivity to some pesticides.

17 rs is essential for more control of residual pesticides.

18 sk to remove trace organic compounds such as pesticides.

19 rs into the environmental risk assessment of pesticides.

20 veloping matrix-matched calibration for many pesticides.

21 ops provide forage for bees but also contain pesticides.

22 imum Residue Levels (MRLs) to control use of pesticides.

23 te, multiplex, highly sensitive detection of pesticides.

24 mmercial basis to reduce the use of chemical pesticides.

25 ical contamination with endocrine-disrupting pesticides.

26 ement method was less than 14% for all three pesticides.

27 to predict the t(R) of an external set of 57 pesticides.

28 and animals but also for crop protection as pesticides.

29 e contamination by chemical products such as pesticides.

30 LOQs for most pesticides (386/400 or 96.5%) were below 10 ug/kg, i.e.,

31 ted analysis, confirming the presence of two pesticides, a plasticizer, and a cannabidiol degradation

32 Exposure by overspray led to greater pesticide accumulation in the eggshell or content than e

33 Combination of pesticides; acetamiprid, flutolanil and etofenprox are u

34 integrative regime were investigated for 12 pesticides across a range of environmentally relevant co

35 Banning highly hazardous pesticides across the 14 countries studied could result

36 ed for drinking supply were analyzed for 109 pesticides (active ingredients) and 116 degradates.

37 We applied the model to nine current-use pesticides, all with in vitro evidence for anti-androgen

38 phallaxis, (2) males had better tolerance to pesticides although they are smaller, and (3) pesticides

39 Pharmaceuticals and pesticides, among other compounds of daily use, such as

40 The decrease in pesticide amounts was lower for the stored samples.

41 oil (3.1-13.7 times higher, depending on the pesticide and target sample).

42 tive models to investigate relations between pesticides and 6 metrics of benthic community structure.

43 in 82% of the samples, with a maximum of 23 pesticides and a median of five compounds per sample.

44 mutants selected from the coexposure to both pesticides and ampicillin.

45 se, six cereal matrices were spiked with 134 pesticides and analysed in two independent labs; a high

46 Intense selection by pesticides and antibiotics has resulted in a global epid

47 We herein describe a mixture of phthalates, pesticides and bisphenol A (mixture N1) detected in preg

48 The combined effects of pesticides and food stress could be predicted best with

49 Allergens, mycotoxins, pesticides and heavy metals are the chemical hazards of

50 Other pesticides and herbicides did not contribute to photolum

51 ong with reuse of most water, minimal use of pesticides and herbicides, and no nutrient losses.

52 ace determination of selected organochlorine pesticides and hormones by gas chromatography mass spect

53 ntensity-weighted lifetime days (IWDs) of 38 pesticides and incident RCC in the Agricultural Health S

54 ofilms also have the potential to accumulate pesticides and may be consumed by aquatic organisms.

55 The approach was validated by quantifying pesticides and mycotoxins in six different cereal sample

56 Chemicals related to crops (pesticides and nutrients) and residential uses (pyrethro

57 time-averaged, quantitative determination of pesticides and other organic pollutants in whole water i

58 The analyzed data set comprises 50 different pesticides and pesticide metabolites that were analyzed

59 ts of the environmental fates and impacts of pesticides and pharmaceuticals, and for providing guidan

60 analyzed to assess occurrence of hydrophobic pesticides and risks to aquatic communities.

61 We evaluated the lifetime use of individual pesticides and the incidence of RCC.

62 microbial responses to exposures to chemical pesticides and the possible implications for mosquito ec

63 Pyrethroid pesticides and their metabolites were not detected.

64 as pharmaceuticals, flavourings, fragrances, pesticides, and biofuels.

65 bes represent an alternative to fertilizers, pesticides, and direct genetic modification of plants.

66 ed polychlorinated biphenyls, organochlorine pesticides, and polybrominated diphenyl ethers in mother

67 f ground-nesting species can be exposed when pesticide applications occur during laying or incubation

68 alth Study, a prospective cohort of licensed pesticide applicators in Iowa and North Carolina.

69 chemicals that may influence RCC risk among pesticide applicators.

70 National bans of highly hazardous pesticides are a potentially cost-effective and affordab

71 Pesticides are a ubiquitous component of conventional cr

72 Neonicotinoid pesticides are agonists of insect nicotinic cholinergic

73 Highly hazardous pesticides are among the leading causes of death by suic

74 Copper (Cu(2+))-containing pesticides are commonly used in agriculture to control f

75 Organophosphate pesticides are frequently used to eliminate or prevent i

76 suggest that monarch responses to host-plant pesticides are largely sublethal and more pronounced in

77 Urban-use pesticides are of increasing concern as they are widely

78 As pesticides are often used concomitantly with other agroc

79 Conventionally, harmful pesticides are used to contain anthracnose disease with

80 Pesticides are widely used in agriculture despite their

81 s, such as chemical warfare nerve agents and pesticides, are known to cause neurological damage.

82 physostigmine presence of other interfering pesticides as high sensitivity and selectivity.

83 ve standard deviation values (<20%) for most pesticides at three spiked levels.

84 plished CSIA for degradation of a persistent pesticide, atrazine, during cultivation of Arthrobacter

85 ic planning (WHO-CHOICE) methods to estimate pesticide-attributable suicide rates for 100 years from

86 icides have led to substantial reductions in pesticide-attributable suicides across several countries

87 Existing pesticide-based Varroa controls are not sustainable.

88 ization rates vary significantly for certain pesticides (but not all) when applied to plants at diffe

89 Atrazine is a widely used pesticide, but the role of the microbiome metabolism of

90 m the need to more control on application of pesticides by farmers, simple and effective postharvest

91 Many pesticides can antagonize the androgen receptor (AR) or

92 rces and release histories, even though both pesticides can be associated with the same land use.

93 f the suspect and non-targeted screening for pesticides can be made quantitative with the aid of in s

94 esticides although they are smaller, and (3) pesticides can cause additional mortality after the stan

95 nteractive effects of serial exposure to the pesticide chlorpyrifos and to a heat spike in the larvae

96 f +3 degrees C) and a chemical stressor (the pesticide chlorpyrifos at 30 ug L(-1)) induced similar d

97 d for sensitive detection of organophosphate pesticide chlorpyrifos in the food chain.

98 partition coefficients of three semivolatile pesticides (chlorpyrifos, pyrimethanil, and trifluralin)

99 ate effects of 12 pesticides, nested in four pesticide classes (chloroacetanilides, triazines, carbam

100 centrations of 12 pesticides, nested in four pesticide classes and two pesticide types.

101 Pesticides commonly contaminate the aquatic environments

102 Six pesticide compounds and 1.6% of wells had concentrations

103 Therefore, although pesticide compounds occurred frequently, concentrations

104 Among the 41% of wells where pesticide compounds were detected, nearly two-thirds con

105 These three pesticides comprised at least 50% of total OCP at each s

106 The use of novel pesticides containing nanomaterials (nanopesticides) is

107 At least two pesticides contaminated the honey and beeswax samples si

108 ification systems (BPSs) treat farm-produced pesticide-contaminated wastewater to reduce surface wate

109 Although pesticide contamination in agricultural surface waters i

110 ustom electronic reader capable of reporting pesticide contamination.

111 Fluralaner is a relatively new pesticide currently sold for control of fleas, ticks, an

112 across the United States to analyze for >100 pesticide degradates and to provide human-health context

113 xploiting molecular biology data to simulate pesticide degradation in soils.

114 so reveals a hysteretic relationship between pesticide degradation rates and gene expression, implyin

115 osquito gut bacterial diversity by enriching pesticide-degrading bacterial communities over susceptib

116 (t(R)) of a large Compound DataBase (CDB) of pesticides detected in fruits and vegetables.

117 Of 31 current-use pesticides detected, 20 were detected more frequently in

118 study reports a method for propoxycarbazone pesticide determination including its metabolite in food

119 experiments in which the degradation of the pesticides dichlorophenoxyacetic acid (2,4-D) and 2-meth

120 This investigation shows the pesticide distribution and reduction using three common

121 ments and the possible mechanisms of loss of pesticides during food processing.

122 these findings, we discuss more broadly how pesticide effects on pollinator cognition might be studi

123 Such pesticide exposure can harm bees, but our understanding

124 Thus, pesticide exposure causes functional, inherited changes

125 s and would be similar to the risk evoked by pesticide exposure.

126 e (OP) intoxications from nerve agent and OP pesticide exposures are managed with pyridinium aldoxime

127 We conclude that short episodes of sublethal pesticide exposures during development are sufficient to

128 ork, we predicted the impact of time-varying pesticide exposures on the survival of gammarids in a sm

129 onfounding factors, with lagged and unlagged pesticide exposures.

130 f the linear and complex interactions in the pesticide extraction methods.

131 Seven pesticides (fludioxonil, cyprodinil, dimethomorph, imaza

132 was developed for the determination of polar pesticides (fosetyl-Al and its metabolite, phosphonic ac

133 The increased demand for pesticide-free foods has also increased the search for h

134 ay be exposed to potentially toxic levels of pesticides from beef cattle feed yards.

135 ce was characterized for the analysis of 204 pesticides from wastewater treatment facility (WWTF) pro

136 ionized water, where 90% of the quantifiable pesticides had a determination coefficient (R(2)) of 0.9

137 Exposure assessment of pesticides has substantially improved over time, with me

138 Maximum residue limits (MRLs) for pesticides have been established in teas for quality con

139 llinators have been declining worldwide, and pesticides have contributed to these declines.

140 ional bans of acutely toxic highly hazardous pesticides have led to substantial reductions in pestici

141 l, the loss rates of vapor phase chlorinated pesticides have slowed by about a factor of 2 between 19

142 used to control disease (e.g. application of pesticides) have significant agricultural, economic, and

143 agrochemical diversity and in general higher pesticide hazard quotients than those from mountain site

144 ported for the detection of pharmaceuticals, pesticides, heavy metals and other contaminants in water

145 used in antimicrobial and anticancer drugs, pesticides, herbicides or fungicides.

146 ommercial products, such as pharmaceuticals, pesticides, herbicides, and crop protection agents.

147 d (Brevicoryne brassicae L.), exposed to the pesticide imidacloprid.

148 ive alternative to the use of transgenics or pesticides in agriculture is the use of a 'green' altern

149 orbent (MEPS) for selective determination of pesticides in apple juice.

150 trumental choice for a multiresidue panel of pesticides in apple, blueberry, grape, and strawberry th

151 essment measured 93 current-use and 3 legacy pesticides in bed sediment and biofilm from 54 small str

152 Pesticides in biofilm improved fit in 4 of the 6 models,

153 The implication of neonicotinoid (neonic) pesticides in contributing to declines of nontarget spec

154 nt linearity was obtained for 168 of the 204 pesticides in deionized water, where 90% of the quantifi

155 howed suitable for the rapid detection of OP pesticides in food matrices with a total assay time of 2

156 dispersive liquid-liquid micro-extraction of pesticides in food samples for the period starting from

157 echnique or complement to LC confirmation of pesticides in fruit matrices.

158 od for the simultaneous determination of 250 pesticides in processed fruit using ultra-performance li

159 rometry techniques to accelerate analysis of pesticides in produce, with technique validation via chr

160 are successfully applied for estimating the pesticides in pure and commercial forms and field sample

161 ofilm improved fit in 4 of the 6 models, and pesticides in sediment improved fit in 2.

162 Thus, antibiotics often coexist with pesticides in some environments.

163 Its application to the analysis of the same pesticides in the individual dried fruits provided good

164 t provides the base for the detection of the pesticides in trace level.

165 The results reveal that (1) the exposure to pesticides (in mg/L) alone led to the emergence of mutan

166 istance to streptomycin; (2) the exposure to pesticides (in mug/L) together with a subinhibitory leve

167 ultiple substances (i.e., drugs of abuse and pesticides) in complex matrices.

168 in situ biodegradation of xenobiotics, like pesticides, in natural and engineered environments is po

169 munities and ecosystem functions and linking pesticide-induced changes in functional groups of organi

170 this study, we exposed monarch larvae to six pesticides (insecticide: clothianidin; herbicides: atraz

171 The Pesticide Loss via Volatilization model was developed to

172 The effects of toxicants, such as pesticides, may be more severe for some life stages of a

173 ta set comprises 50 different pesticides and pesticide metabolites that were analyzed in 3741 samples

174 hods based on QuPPe-PO approach (Quick Polar Pesticides Method for products of Plant Origin) were opt

175 rison with the reference method (Quick Polar Pesticides Method), confirming the method fitness-for-pu

176 insufficiently sensitive for at least seven pesticides (metsulfuron-methyl, terbutryn, imidacloprid,

177 reduced from 1500 to 9, and among them, two pesticides (mexacarbate, 17 ng/L, and fenpropidin, 23 ng

178 When calibrating against data on pesticide mineralization, the gene-centric and biomass-b

179 pturing microbial dynamics and in predicting pesticide mineralization.

180 complex samples, as exemplarily shown for a pesticide mixture and a tryptic digest.

181 Combined exposure to the three-pesticide mixture and N. ceranae reduced bumblebee colon

182 nt efforts to include the additional risk of pesticide mixtures and environmental stressors into the

183 Exposure to pesticide mixtures reduced food collection by bumblebees

184 Pesticide mixtures were present in 82% of the samples, w

185 N. ceranae when they had not been exposed to pesticide mixtures, and bumblebees exposed to the fungic

186 ging to the Great Barrier Reef carry complex pesticide mixtures.

187 r disrupt intermolecular attractions between pesticide molecules and soil.

188 For pesticides monitoring, samples were separated into store

189 ecological risk assessment of these emerging pesticides necessitates an understanding of the fate of

190 pond communities, we evaluate effects of 12 pesticides, nested in four pesticide classes (chloroacet

191 systems to standardized concentrations of 12 pesticides, nested in four pesticide classes and two pes

192 sphate flame-retardant metabolites, phenols, pesticides, nitro and nitroso compounds, and per- and po

193 atmospheric deposition of 36 organochlorine pesticides (OCPs) and 7 industrial compounds (OCICs) by

194 rganic pollutants, especially organochlorine pesticides (OCPs) and polychlorinated biphenyls (PCBs),

195 chlorinated biphenyls (PCBs), organochlorine pesticides (OCPs), polybrominated diphenyl-ethers (PBDEs

196 diphenyl ethers (PBDEs), and organochlorine pesticides (OCPs).

197 Atrazine, a class 3a carcinogen, is a pesticide of chloro triazine family and is known to seve

198 l, deployment of virus-free 'clean seed' and pesticide on crop yield and disease status of individual

199 Overall, we found no impact of any pesticide on immature development time and relatively we

200 By demonstrating consistent effects of pesticides on communities and ecosystem functions and li

201 Effects of pesticides on ecosystem function are mediated by alterat

202 e effects of the co-occurring, nonantibiotic pesticides on the development of antibiotic resistance,

203 Washing and soaking water reduce pesticides only 0.40 to 4.28%.

204 ood production, residues of organophosphorus pesticides (OPs) are more frequently found in the enviro

205 and fentanyl), anesthetics, neurotoxins, the pesticide paraquat, and heparin anti-coagulants by the P

206 tions studying diverse contaminants (such as pesticides, pharmaceuticals, and energetic compounds) we

207 Field results indicate pesticide pollution is ubiquitous at levels above toxici

208 ed polychlorinated biphenyls, organochlorine pesticides, polybrominated diphenyl ethers in fat, and p

209 ver, applications of SPR in the detection of pesticide, polycyclic aromatic hydrocarbons (PAHs), heav

210 s in order to enhance their greenness during pesticide pre-concentration in food samples.

211 mpling by identification of more current-use pesticides present and better estimation of ecological r

212 tion in heat tolerance was stronger when the pesticide pulse followed the heat spike, and was buffere

213 Of 16 different pesticides quantified in particulate matter samples coll

214 The pesticide reduction during cooking were 20.73 to 57.72%,

215 environmental risk assessment conducted for pesticide registration in the European Union (EU), avian

216 Pathogens and pesticides represent important stressors that influence

217 Eighty-seven pesticides representing over 28 classes were detected.

218 ly improve the efficiency and sensitivity of pesticide research and evaluation, and thus the sustaina

219 s is considered as the essential step in the pesticide residue analysis, as it provides the base for

220 eding water was screened for heavy metal and pesticide residue contamination.

221 t is, however, challenging to quantify multi-pesticide residues at low concentrations in complex matr

222 rocessing are evaluated of the removal of 16 pesticide residues in canned apricots and peaches and in

223 ng techniques to reduce the concentration of pesticide residues in curry leaf were evaluated and foun

224 dapted for simultaneous determination of 400 pesticide residues in green tea products using ultra per

225 can be applied for routine analysis of multi-pesticide residues in green tea.

226 Pesticide residues in wax, honey and beebread samples we

227 However, recent studies report pesticide residues on milkweed leaves that could act as

228 st effective clean-up method and enabled 225 pesticide residues to be quantified, based on solvent ca

229 Other pesticide residues were detected in beeswax and bee brea

230 ed fruits, detecting the presence of several pesticide residues, such as fluopyram, spinosad or cypro

231 tions, which will enable producers to reduce pesticide residues.

232 enhance food safety from potentially harmful pesticide residues.

233 and cobalamin with insignificant amounts of pesticide residues.

234 or simultaneous estimation of the concerning pesticides' residues using simple economic steps of fiel

235 Generally, pesticides, residues could be one of the health hazard s

236 -active study of resistance evolution across pesticide resistance disciplines.

237 nvasion rate, interspecific competition, and pesticide resistance.

238 tions for current practices and policies for pesticide risk assessment and use as the combinations te

239 or pollination, and ensuring that regulatory pesticide risk assessment frameworks are protective of t

240 anagement strategy requires an evaluation of pesticide risk for pollinator species.

241 acent to watersheds with high fertilizer and pesticide runoff promote low levels of growth anomalies,

242 ardous pesticides to prevent suicides due to pesticide self-poisoning, compared with a null comparato

243 h proportion of suicides are attributable to pesticide self-poisoning, reaching a cost-effectiveness

244 friendly, portable and rapid electrochemical pesticide sensing system is presented that can screen fo

245 les from microcosms treated with each of the pesticides, separately.

246 Our experiment shows that egg spraying with pesticides should be considered as a relevant exposure s

247 Many pesticides show a pronounced biphasic degradation in soi

248 n and independent action were applied to the pesticide SSDs, focusing on environmental threshold valu

249 ated using collected data, and evaluated for pesticide storm load and concentrations under several ma

250 The method shows good linearity for the 16 pesticides studied (R2 > 0.999); it is accurate and prec

251 ing that the potential consumer risk for the pesticides studied is practically negligent for human he

252 rthropod and pathogen pests results in lower pesticides, suggesting that the introduced status of som

253 hazardous pesticides to reduce the burden of pesticide suicides.

254 Exposure to either pesticide through contact with treated soils did not aff

255 ME) devices to further elucidate the fate of pesticides through the WWTF process.

256 endent on rice as a staple food and chemical pesticides to control pests is the dominant paradigm in

257 ages have been proposed as an alternative to pesticides to kill bacterial pathogens of crops.

258 lementing a national ban of highly hazardous pesticides to prevent suicides due to pesticide self-poi

259 plementing national bans of highly hazardous pesticides to reduce the burden of pesticide suicides.

260 diphenyl ethers (PBDEs), and organochlorine pesticides) to comprehensively assess their current POP

261 cal control using lampricides (i.e., lamprey pesticides) to target larval sea lamprey and barriers to

262 The new pesticide toxicity assessment protocol showed that (1) a

263 ures is pivotal for realistic predictions of pesticide toxicity.

264 sampling date (day 3 vs. day 7), but not by pesticide treatment.

265 However, accounting for pesticide-triggered gene regulation allows improved perf

266 istic understanding of microbial controls on pesticide turnover in soils.

267 orm models of coupled microbial dynamics and pesticide turnover with measurements of the abundance an

268 azines, carbamates organophosphates) and two pesticide types (herbicides, insecticides) applied at st

269 es, nested in four pesticide classes and two pesticide types.

270 rnaround time for analyzing a large panel of pesticides, ultimately providing us the opportunity to e

271 We tested the hypothesis that variation in pesticide use among crop species is a function of crop e

272 , explaining roughly half of the variance in pesticide use among crops against pathogens and herbivor

273 Agricultural work and occupational pesticide use have been associated with increased risk o

274 the importance of integrative approaches to pesticide use monitoring.

275 mobilizing sorbed arsenic derived from past pesticide use or other sources.

276 example, with a 10-fold increase in total OP pesticide use within 1 km of maternal residence during p

277 s in the native plant flora received greater pesticide use, explaining roughly half of the variance i

278 vulnerability to disease and parasites, and pesticide use.

279 Reduced pesticides use, alongside increased organic farming, has

280 ows the user to adjust the properties of the pesticide, various soil and plant descriptors, and clima

281 lues were then used as input parameters in a pesticide volatilization model to understand how their v

282 odel was developed to predict and understand pesticide volatilization rates from a planted agricultur

283 to understand how their variability affects pesticide volatilization rates under different condition

284 The model showed that most pesticides volatilize more readily from plants than from

285 onducted at ~24 degrees C indicated that all pesticides volatilized more readily in the presence of a

286 l chemicals, including organophosphorus (OP) pesticides, warfare agents and drugs, are AChE reversibl

287 r the trace determination of pyridaphenthion pesticide was developed in this study.

288 ultural impacts, in addition to the expected pesticides, wastewater-derived chemicals and chemicals t

289 Cu-SWCNT-Pc hybrid towards to physostigmine pesticide were performed.

290 On average, 4 times as many current-use pesticides were detected in biofilm at a site (median of

291 Residues of 21 pesticides were determined in honey.

292 e the concentrations of veterinary drugs and pesticides were measured by ultra-fast liquid chromatogr

293 Although real-case exposures to individual pesticides were predicted to produce little to no impact

294 Pesticides were quantified using matrix-matched calibrat

295 available CDB was properly curated, and the pesticides were represented by conformation-independent

296 Transformation products of pesticides were tentatively identified, including two no

297 Thirteen micropollutants, including four pesticides, were only detected in posthurricane samples.

298 latilization rates of plant- and soil-sorbed pesticides whereas LAI, h(leaf), and the percent of wate

299 Vinclozolin is a pesticide with antiandrogenic activity as an endocrine d

300 to protect sensitive species from urban-use pesticides with low environmental effect concentrations.