ライフサイエンスコーパス: chlorpyrifos

1 idation by increasing times, especially with chlorpyrifos.

2 dieldrin, trans-chlordane, endosulfan I, and chlorpyrifos.

3 ection; and the organophosphate insecticide, chlorpyrifos.

4 ption factors in the presence and absence of chlorpyrifos.

5 phosphate insecticides such as parathion and chlorpyrifos.

6 to low, was imidacloprid, thiamethoxam, and chlorpyrifos.

7 (>20), notably methiocarb, formetanate, and chlorpyrifos.

8 hrin, N,N-diethyl-meta-toluamide (DEET), and chlorpyrifos.

9 se in immunoassay for sensitive detection of chlorpyrifos.

10 o-analytical transducer for the detection of chlorpyrifos.

11 smaller larvae, which were more sensitive to chlorpyrifos.

12 ile they contained residuals of diazinon and chlorpyrifos.

13 ese quail liver tissue following exposure to chlorpyrifos (0, 0.04, 0.1, 0.2, 0.4, 1, 2, 4, 10, 20, a

14 ntrations ranged from 9.2 to 199 ng/m(3) for chlorpyrifos, 0.03 to 20 ng/m(3) for chlorpyrifos-oxon,

15 iring endotracheal intubation (66 of 439 for chlorpyrifos, 15.0%; 93 of 264 for dimethoate, 35.2%, OR

16 r conception were 2.2 (95% CI: 0.7, 6.5) for chlorpyrifos, 2.3 (95% CI: 0.98, 5.3) for organophosphat

17 from the market in 1972), chlordane (1988), chlorpyrifos (2001), and diazinon (2004).

18 ganophosphate neurotoxicity, were dosed with chlorpyrifos (3 mg/kg per day, orally, from day 2 to day

19 residential use: chlordane (-15% per year), chlorpyrifos (-31%), diazinon (-48%), and propoxur (-34%

20 Compared with chlorpyrifos (35 of 439, 8.0%), the proportion dying was

21 In 1990, there were 1.36 million kg of chlorpyrifos, 4.67 million kg of diazinon and 1.23 milli

22 Rat dams were exposed to chlorpyrifos (5 mg/kg) or vehicle on gestational days 18

23 ribenuron-methyl, metribuzin, profenofos and chlorpyrifos, 5.0 to 1500.0 ng mL(-1) for phosalone, and

24 (15 mug/kg), methamidophos (50 mug/kg), and chlorpyrifos (93 mug/kg) were measured in licorice, mall

25 Chlorpyrifos (98.7%), cis- and trans-permethrin (97.5%),

26 evant concentrations in soils and sediments, chlorpyrifos, a hydrophobic organic insecticide, showed

27 Likewise, chlorpyrifos, a pesticide often encountered in coral-ree

28 ed is ecologically advantageous, exposure to chlorpyrifos, a pesticide often inadvertently added to c

29 Exposure to chlorpyrifos affected the key body stoichiometric ratios

30 ty in significantly potentiating another OP, chlorpyrifos, against the common pest, the peach-potato

31 A measured average decrease of 18% in chlorpyrifos air concentrations indicates the residence

32 States in 2001 to determine the decreases in chlorpyrifos air concentrations over a one-year period.

33 -dinitro-o-cresol, ethylacrylate, malathion, chlorpyrifos, aldicarb, carbofuran, carbaryl, 2,4-dichlo

34 udy where 10% of them was found positive for chlorpyrifos, ametryn and metalaxyl.

35 f gold nanoparticles (AuNPs) when exposed to chlorpyrifos, an agricultural pesticide, and its applica

36 ronmental pollutants to test the system were chlorpyrifos, an organophosphate pesticide, and tetrabro

37 Indoors, only 78% of air samples for chlorpyrifos and 35% of samples for azinphos-methyl were

38 For example, all outdoor air samples for chlorpyrifos and 97% of samples for azinphos-methyl were

39 oor and outdoor air concentration ratios for chlorpyrifos and azinphos-methyl were 0.17 and 0.44, res

40 anazine, and paraquat) and two insecticides (chlorpyrifos and chlordane).

41 Therefore, we exposed damselfly larvae to chlorpyrifos and cues from predatory dragonflies and foc

42 ectively), and two widely used insecticides, chlorpyrifos and diazinon (OR = 1.0, 1.1, 1.7, 1.9; p(tr

43 The insecticides parathion, chlorpyrifos and diazinon are bioactivated to potent cho

44 Superimposed on this pattern, chlorpyrifos and diazinon were surprisingly the least al

45 To resolve the disparities between chlorpyrifos and diazinon, we performed analyses in rat

46 nger resemblance of these two agents than of chlorpyrifos and dieldrin.

47 ree insecticides tested, lambda-cyhalothrin, chlorpyrifos and emamectin benzoate induced susceptible

48 lso analysed, finding residues of metalaxyl, chlorpyrifos and iprodione in some of them.

49 erved for example with the major insecticide chlorpyrifos and its bioactivated metabolite chlorpyrifo

50 ndent developmental neurotoxicant actions of chlorpyrifos and its differences from diazinon, while at

51 ted on alfalfa fields using the insecticides chlorpyrifos and lambda-cyhalothrin.

52 term desorption may explain the detection of chlorpyrifos and other hydrophobic organic compounds in

53 This effect was specific to chlorpyrifos and parathion and was not affected by syner

54 stance air flow, but showed lower amounts of chlorpyrifos and PCA, suggesting local sources of these

55 veloped method was applied for estimation of chlorpyrifos and prophenofos and it was found that the c

56 ic method for the simultaneous estimation of chlorpyrifos and prophenofos in vegetables and fruits.

57 In UV method, the absorbance of chlorpyrifos and prophenofos was measured at wavelength

58 effects of serial exposure to the pesticide chlorpyrifos and to a heat spike in the larvae of the mo

59 rimination of a binary mixture of pesticide (chlorpyrifos) and herbicide (glyphosate).

60 organophosphates (parathion, malathion, and chlorpyrifos), and one thiocarbamate (S-ethyl-dipropylth

61 A rapid analysis of acephate, chlorpyrifos, and cyazofamid in tomato peels during pre-

62 end of the pre-harvest intervals, acephate, chlorpyrifos, and cyazofamid were determined at 0.86, 0.

63 ulfan isomers, p,p'-DDD, alpha-cypermethrin, chlorpyrifos, and diazinon residues in the range of 0.56

64 Latitudinal trends of alpha-endosulfan, chlorpyrifos, and dicofol in seawater were roughly consi

65 ulation test with polychlorinated biphenyls, chlorpyrifos, and four marine benthic invertebrates.

66 41 +/- 9 ng/g for the high chlorpyrifos, low chlorpyrifos, and lambda-cyhalothrin transfer experiment

67 nophosphate insecticides (terbufos, fonofos, chlorpyrifos, and phorate) were elevated when these chem

68 trends were observed for chlorimuron-ethyl, chlorpyrifos, and phorate; the strongest odds ratio was

69 l data sets of three analytes (rhodamine 6G, chlorpyrifos, and triclosan), which are then used to tra

70 e, BXRalpha-specific agonists such as 4-ABB, chlorpyrifos, and trifluralin act as antagonists on BXRb

71 of chlorpyrifos oxon, the activated form of chlorpyrifos, and were more sensitive to chlorpyrifos it

72 spective antibody glyphosate on one side and chlorpyrifos antibody on other side.

73 2.0; 95% CI: 1.1, 3.6), and second-trimester chlorpyrifos applications (OR = 3.3; 95% CI: 1.5, 7.4).

74 Imidacloprid, thiamethoxam, and chlorpyrifos are three of common pesticides known for se

75 K(leaf-air) values for chlorpyrifos as an active ingredient alone decreased wit

76 us pesticides (OPPs), including diazinon and chlorpyrifos as model analytes in various samples.

77 s and foliar penetration for the insecticide chlorpyrifos (as an active ingredient alone and in a pes

78 es C) and a chemical stressor (the pesticide chlorpyrifos at 30 ug L(-1)) induced similar defects by

79 sampling for indoor and outdoor exposures to chlorpyrifos, azinphos-methyl, and oxygen analogs in a r

80 of the ollowing organophosphorus pesticides: chlorpyrifos, azinphos-methyl, and their oxygen analogs

81 r penetration increased with temperature for chlorpyrifos both as an active ingredient and in the for

82 ultra-sensitive sensor for trace analysis of chlorpyrifos by ECL technique.

83 ted to determine seven acaricides (atrazine, chlorpyrifos, chlorfenvinphos, alpha-endosulfan, bromopr

84 ogy to determine seven pesticides (atrazine, chlorpyrifos, chlorfenvinphos, alpha-endosulfan, bromopr

85 iso-OMPA) and five AChE inhibitors diazinon, chlorpyrifos, chlorfenviphos, parathion, and aldicarb.

86 icantly higher outdoor air concentrations of chlorpyrifos, chlorpyrifos-oxon, and azinphos-methyl tha

87 stablished that plasma PON1 protects against chlorpyrifos/chlorpyrifos-oxon and diazinon/diazoxon (DZ

88 n of spiked pesticides Glyphosate (Glyp) and Chlorpyrifos (Chlp) in low-fat and high-fat food matrix.

89 efore and after exposure to the OP pesticide chlorpyrifos (CHP) in adult female rats implanted with t

90 es of the season) including the insecticides chlorpyrifos, clothianidin, avermectin, thiamethoxam, an

91 Chlorpyrifos coexposure augmented BaP inhibition of cell

92 redicts that the T allele acts by decreasing chlorpyrifos concentration in the compartment targeted i

93 f NaCl, AuNPs undergo agglomeration at lower chlorpyrifos concentrations but aggregation at higher co

94 Chlorpyrifos concentrations in pore water of spiked sedi

95 Toxicity studies were performed using the chlorpyrifos concentrations in the range of those propos

96 This approach can be tailored for various chlorpyrifos concentrations not only in cucumbers but al

97 affected the key body stoichiometric ratios: chlorpyrifos consistently increased N:P, while its effec

98 ion, (2) estimation of ALP in saliva and (3) chlorpyrifos control in commercial preparations.

99 o efficiently extract two target pesticides; chlorpyrifos (CPF) and triazophos (TAP) from orange juic

100 r 10 mug/L of the organophosphorus pesticide chlorpyrifos (CPF) from hatching to metamorphosis.

101 The widespread use of chlorpyrifos (CPF) has raised major concerns about its p

102 ified the negative impact of the insecticide chlorpyrifos (CPF) in larvae of low- and high-latitude p

103 presents a novel method for the detection of chlorpyrifos (CPF) in lemon juice and goat milk using a

104 uild an electrochemical sensor for detecting Chlorpyrifos (CPF) in vegetable sample solutions.

105 Chlorpyrifos (CPF) is one of the most widely used insect

106 nti-cholinesterase organophosphate pesticide chlorpyrifos (CPF) on the refractive development of the

107 two additional pesticides thiram (TMTD) and chlorpyrifos (CPF) were 86.32 %-112.47 %.

108 Prenatal exposure to chlorpyrifos (CPF), an organophosphate insecticide, is a

109 NDO-II, and ENDO SUL), chlorothalonil (CHT), chlorpyrifos (CPF), and trifluralin (TFN).

110 e commonly-used organophosphate insecticide, chlorpyrifos (CPF), impairs brain cell development, axon

111 ng/L with sensitivity 0.41 mA/ng/L/cm(2) for chlorpyrifos (CPF); and 10.2 ng/L with sensitivity 0.58

112 horus pesticides (OPPs), diazinon (DIZ), and chlorpyrifos (CPS) from the diverse aqueous media follow

113 s): trifluralin, endosulfan, chlorothalonil, chlorpyrifos, dacthal, and dicofol.

114 Chlorpyrifos degraded at a rate similar to the dark cont

115 Chlorpyrifos desorption followed a nonsingular falling d

116 oratory experiment, tissue concentrations of chlorpyrifos detected in ELL were associated with reduce

117 The insecticide chlorpyrifos detected in snail tissues was negatively co

118 st pesticide levels were below EU MRLs, some chlorpyrifos detections exceeded MRLs.

119 We exposed PC12 cells to chlorpyrifos, diazinon or parathion in the undifferentia

120 e compared two organophosphate insecticides (chlorpyrifos, diazinon) with an organochlorine (dieldrin

121 of neuroactive peptides by organophosphates (chlorpyrifos, diazinon), an organochlorine (dieldrin) an

122 We compared organophosphates (chlorpyrifos, diazinon), an organochlorine (dieldrin) an

123 (LP(50) <= 10) toxicities for azoxystrobin, chlorpyrifos, diazinon, and imidacloprid, while risk to

124 trophenol, alachlor, atrazine, azoxystrobin, chlorpyrifos, diazinon, diuron, endosulfan, fenthion, fo

125 Six OPs including chlorpyrifos, diazinon, fenitrothion, methyl parathion,

126 sing in vivo studies from the literature for chlorpyrifos, diazinon, fenitrothion, methyl-parathion,

127 five individual organophosphates (acephate, chlorpyrifos, diazinon, malathion, and oxydemeton-methyl

128 Among the tested pesticides, chlorpyrifos, diazinon, malathion, phosalone, propargite

129 opmental neurotoxicants-manganese, fluoride, chlorpyrifos, dichlorodiphenyltrichloroethane, tetrachlo

130 Three organophosphate pesticides, chlorpyrifos, dichlorvos, and dicrotophos, were used as

131 While chlorpyrifos did not have any effect at the intermediate

132 eight pesticides (desulfinylfipronil, AMPA, chlorpyrifos, dieldrin, metolachlor, atrazine, CIAT, gly

133 he lowest observed effect concentrations for chlorpyrifos, dieldrin, trifluralin, and p,p'-dichlorodi

134 Further, the effects of chlorpyrifos differed substantially depending on whether

135 Thiamethoxam, captan, chlorpyrifos, dimethoate and pyrimethanil were found in

136 We prospectively studied 802 patients with chlorpyrifos, dimethoate, or fenthion self-poisoning adm

137 Chlorpyrifos dominated OCP flux at Lomonosovfonna (81.7

138 n 1999 in Culex pipiens mosquitoes surviving chlorpyrifos doses 1 mg l(-1) and more recently found in

139 rats were given apparently subtoxic doses of chlorpyrifos either on postnatal days 1-4 or 11-14 and t

140 Chlorpyrifos, EPTC, paraquat, and parathion demonstrated

141 Chlorpyrifos evoked by far the largest effect, with wide

142 Chlorpyrifos evoked robust upregulation of cholecystokin

143 Again, chlorpyrifos evoked stage-specific changes in transcript

144 Chlorpyrifos evoked stage-specific interference with the

145 Although chlorpyrifos exerts some effects through cholinesterase

146 tial for electrochemical detection of the OP chlorpyrifos, exhibiting a wide linear detection rangefr

147 These results support the hypothesis that chlorpyrifos exposure in ELL reduced the density of snai

148 ess this, we used a rat model of gestational chlorpyrifos exposure to interrogate the alterations in

149 ed at the low concentration when exposure to chlorpyrifos followed the heat spike.

150 , the most frequently studied exposures were chlorpyrifos ([Formula: see text]), mercury ([Formula: s

151 rocessing the plants previously treated with chlorpyrifos formulations.

152 Local wind observations indicated that the chlorpyrifos found at Temple Basin primarily came from t

153 icability of the device for the detection of chlorpyrifos from the real vegetable sample was also tes

154 action (SPME) for extracting trifluralin and chlorpyrifos from vegetables, fruit samples, and wastewa

155 In 2015, less toxic pesticides (chlorpyrifos, glyphosate, carbofuran, and carbaryl) were

156 women who had ever used the organophosphates chlorpyrifos [HR=1.4 (95% CI: 1.0, 2.0)] or terbufos [HR

157 e and 21.23 %of roasted coffee samples, with chlorpyrifos, imidacloprid, and cypermethrin commonly de

158 sidues were detected, including acrinathrin, chlorpyrifos, imidacloprid, and malathion, with some exc

159 Abamectin, Chlorpyrifos, Imidacloprid, Iprodione, lambda-cyhalothri

160 at thermoneutrality and fed a high-fat diet, chlorpyrifos impairs BAT mitochondrial function and diet

161 y was to investigate abamectin, diazinon and chlorpyrifos in apple from the Mahabad of Iran.

162 age groups except for the pesticide residue chlorpyrifos in cucumber (1.7945).

163 r consumption by Lebanese children, although Chlorpyrifos in cucumber was of concern.

164 , achieves high reproducibility in detecting chlorpyrifos in cucumber, even at concentrations as low

165 mon pyrethroids, pyrethroid metabolites, and chlorpyrifos in floor wipes, and urinary concentrations

166 decreased the concentrations of diazinon and chlorpyrifos in samples exposed to it.

167 soil-air)U values were 328 and 90 kJ/mol for chlorpyrifos in the absence and presence of formulation

168 itive detection of organophosphate pesticide chlorpyrifos in the food chain.

169 erature, while the effects of temperature on chlorpyrifos in the formulation were negligible.

170 ticides (OCPs) and the current use pesticide chlorpyrifos in the Southern Ocean.

171 ctions to end the use of one such pesticide, chlorpyrifos, in agriculture were recently stopped by th

172 rganophosphorus pesticides, azamethiphos and chlorpyrifos, in mineral water and grape samples.

173 their lower net energy budget, moreover the chlorpyrifos-induced inhibition of its target enzyme (ac

174 Notably, the chlorpyrifos-induced mortality was much more magnified b

175 elegans recipient larvae experienced a lower chlorpyrifos-induced mortality when they received an I.

176 Also the chlorpyrifos-induced reduction in heat tolerance was str

177 oorly to pralidoxime treatment compared with chlorpyrifos-inhibited acetylcholinesterase.

178 These results indicate that chlorpyrifos interferes with brain development, in part

179 Chlorpyrifos is a widely used organophosphate insecticid

180 Chlorpyrifos is an organophosphorus pesticide used exten

181 ncentrations indicates the residence time of chlorpyrifos is expected to be 6.9 years and compares we

182 s not predict human toxicity since, although chlorpyrifos is generally the most toxic in rats, it is

183 Gestational, subacute exposure to chlorpyrifos is linked to increased prevalence of neurod

184 tal samples were found positive for ametryn, chlorpyrifos, isoprocarb, and metalaxyl.

185 of chlorpyrifos, and were more sensitive to chlorpyrifos itself.

186 Chlorpyrifos K(soil-air,formulation) values were also me

187 In particular, we recommend chlorpyrifos, lead, and polychlorinated biphenyls (PCBs)

188 s by tracking and modeling chemical flows of chlorpyrifos, linuron, and six PCBs in water-sediment-ma

189 +/- 48 ng/g, and 41 +/- 9 ng/g for the high chlorpyrifos, low chlorpyrifos, and lambda-cyhalothrin t

190 ecticides that have the same mode of action (chlorpyrifos, malathion) or a different mode of action (

191 d biosensors for some common pesticides like chlorpyrifos, malathion, parathion, paraoxon, and carbar

192 the pesticides studied are 2,4-D, atrazine, chlorpyrifos, malathion, permethrin, and propoxur.

193 zole, fludioxinil and cyprodinil, abamectin, chlorpyrifos-methyl, hexythiazox and metalaxyl) initiall

194 Heptachlor epoxide, chlorpyrifos, metolachlor, butachlor, and 2,3',4',5-tetr

195 idation of an analytical method to determine chlorpyrifos (O,O-diethyl O-3,5,6-trichloro-2-pyridyl ph

196 e; the strongest odds ratio was for applying chlorpyrifos on more than 40 days per year (OR = 2.40, 9

197 We assessed the effects of chlorpyrifos on nuclear transcription factors involved i

198 ternal exposure to the developmental insult, chlorpyrifos on the offspring's gene expression via mRNA

199 al on diazinon while they are influential on chlorpyrifos ones.

200 with donor larvae first preexposed to either chlorpyrifos or a solvent control to match the subsequen

201 nce to malathion and cypermethrin but not to chlorpyrifos or permethrin.

202 reterm labor), an organophosphate pesticide (chlorpyrifos), or nicotine.

203 n proteins that had been treated with either chlorpyrifos oxon (CPO) or diisopropylfluorophosphate (D

204 chlorpyrifos and its bioactivated metabolite chlorpyrifos oxon (CPO).

205 They had masses of 1854 and 1967 for chlorpyrifos oxon, 1825 and 1938 for dichlorvos, 1881 an

206 s blocked with diisopropylfluorophosphate or chlorpyrifos oxon, albumin had normal esterase activity

207 Our goal was to determine whether chlorpyrifos oxon, dichlorvos, diisopropylfluorophosphat

208 extremely sensitive to the toxic effects of chlorpyrifos oxon, the activated form of chlorpyrifos, a

209 The detection limits for diazinon(oxon) and chlorpyrifos(oxon) were estimated to be as low as 6 x 10

210 organophosphorus pesticides (diazinon(oxon), chlorpyrifos(oxon)) in aqueous samples with minimized in

211 Both isoforms hydrolyse chlorpyrifos-oxon and phenylacetate at approximately the

212 (3) for chlorpyrifos, 0.03 to 20 ng/m(3) for chlorpyrifos-oxon, < LOD (limit of detection) to 7.3 ng/

213 outdoor air concentrations of chlorpyrifos, chlorpyrifos-oxon, and azinphos-methyl than did samples

214 of the prototypic organophosphorus compound chlorpyrifos-oxon.

215 rmination of endocrine disruptor pesticides (Chlorpyrifos, Penconazole, Procymidone, Iprodione, Bromo

216 Cadusafos, chlorpyrifos, permethrin, and deltamethrin were found in

217 efficients of three semivolatile pesticides (chlorpyrifos, pyrimethanil, and trifluralin) in the abse

218 etection of paraoxon-ethyl, fenitrothion and chlorpyrifos ranging from 1.0 and 10.0mumolL(-1) with a

219 previously shown to affect cell development, chlorpyrifos reduced AP-1, but not Sp1 DNA-binding activ

220 Exposure to chlorpyrifos reduced the fitness of chlorpyrifos-sensiti

221 These results suggest that the presence of chlorpyrifos residues on meat could have a negative effe

222 alone, dichlorvos, diazinon, profenofos, and chlorpyrifos) residues in fruit juice and aqueous sample

223 investigated the genetic determinism of high chlorpyrifos resistance (HCR), a phenotype first describ

224 nd 98.86% were obtained for azamethiphos and chlorpyrifos, respectively.

225 .9987 were also obtained for trifluralin and chlorpyrifos, respectively.

226 pg.m(-2).d(-1)) for gamma-HCH, dieldrin, and chlorpyrifos, respectively.

227 so found exposure-response associations with chlorpyrifos [RRIWD Quartile 4 = 1.68 (95% CI: 1.05, 2.7

228 Through chlorpyrifos selection, we selected several HCR strains

229 osure to chlorpyrifos reduced the fitness of chlorpyrifos-sensitive clones (reduced survival, mass, a

230 ovative enzyme free electrochemiluminescence chlorpyrifos sensor was reported based on the incorporat

231 Myosin protein was exposed to diazinon and chlorpyrifos showing an increase in its oxidation by inc

232 iscover that the organophosphate insecticide chlorpyrifos suppresses UCP1 and mitochondrial respirati

233 ta indicate that the commonly used pesticide chlorpyrifos, suppresses diet-induced thermogenesis and

234 In this study, technical chlorpyrifos (TCPF) and its oil in water (EW) and emulsi

235 Noncholinergic actions of chlorpyrifos that are unique to brain development reinfo

236 o exposure to the organophosphorus pesticide chlorpyrifos that may account for the well-established b

237 compounds (cadmium, lambda-cyhalothrin, and chlorpyrifos) that differentially affected life-history

238 t, the individual and combined toxicities of chlorpyrifos, thiamethoxam, and imidacloprid to bumblebe

239 Then, chicken breast was contaminated with chlorpyrifos to evaluate carbonylation and the effect of

240 We investigated the costs of chlorpyrifos tolerance in Daphnia magna when sequentiall

241 We did not find any costs of chlorpyrifos tolerance in the absence of the stressors a

242 heat spike, the benefit of the evolution of chlorpyrifos tolerance was nullified as the chlorpyrifos

243 ve (hormetic) effects on clones selected for chlorpyrifos tolerance.

244 chlorpyrifos tolerance was nullified as the chlorpyrifos-tolerant clones experienced (stronger) syne

245 a higher mean temperature and DTF magnified chlorpyrifos toxicity in Ischnura elegans damselfly larv

246 damage to lipids, contributed to the higher chlorpyrifos toxicity under DTF.

247 -590 kg), alpha-endosulfan (6.5-200 kg), and chlorpyrifos (up to 1400 kg), as well as dioxin toxic eq

248 es (fenobucarb, diazinon, chlorothalonil and chlorpyrifos) using a randomised factorial design.

249 Air-sea gas exchange of chlorpyrifos varied from net volatilizaiton in East Asia

250 t temperatures below 24.5 degrees C, modeled chlorpyrifos volatilization rates were higher in the pre

251 os and prophenofos and it was found that the chlorpyrifos was 0.018mg/kg, which is above maximum resi

252 Desorption of chlorpyrifos was biphasic in nature, with a labile and n

253 Chlorpyrifos was found in samples from this area for the

254 Next, chlorpyrifos was incubated with PC12 cells either during

255 Chlorpyrifos was observed to decrease mitochondrial basa

256 We conducted a field study after chlorpyrifos was phased out for indoor use in the United

257 elling case that exposure to the insecticide chlorpyrifos was responsible for differences in snail (B

258 In some samples the diazinon and chlorpyrifos were above allowed limit according to World

259 The lethal effects of chlorpyrifos were magnified at the high mean temperature

260 rent-use pesticides (dacthal, triallate, and chlorpyrifos) were frequently found in both air and wate