ライフサイエンスコーパス: POP

1 POP amounts (mg/ha) stored in different tree components,

2 POP concentrations in the plastic did not differ signifi

3 POP formation was highest in shallow-fried potatoes with

4 POP levels varied significantly among sites, more than 3

5 POP plays a central role in regulating cell proliferatio

6 POP were analyzed using a GC-MS method.

7 POPs are suggested to interfere with the interaction bet

8 POPs in soils showed concentrations close to soil-air eq

9 POPs with high TEFs and AhR affinity were associated wit

10 mily microRNAs, affect the activity of LIT-1/POP-1 cellular asymmetry machinery and APR-1 polarity du

11 he cellular polarizing activity of the LIT-1/POP-1 system as development proceeds.

12 the summed molar blood concentrations of 14 POPs were positively related to TAC.

13 This study reports concentrations of 20 POPs (aldrin, chlordane, chlordecone, DDT, dieldrin, end

14 ear organic groups, resulting in a stable 3D POP-MOF framework, which exhibits interesting sorption a

15 rnal and paternal serum concentrations of 63 POPs, comprising five major classes of pollutants, with

16 t instance of carboxypeptidase activity in a POP family member.

17 garine increased POP content in foods with a POP profile characterized by a higher ratio of epoxy- to

18 salmon tissue to differing degrees, acquire POPs from different dietary sources, or bioaccumulate or

19 ding polyethylene (two with plastic additive POPs), styrene acrylonitrile, polystyrene, and nylon and

20 body condition did not significantly affect POP trends.

21 By combining correlations among POP concentrations, differences in tissue concentrations

22 Transfer pathways differed among POPs and traits such as habitat affinity, feeding behavi

23 unravel relationships between age, BMI, and POP concentrations, informing efforts to understand pote

24 Here, we discuss our model of COP- and POP-mediated inflammasome regulation.

25 s in the blood of children with leukemia and POP levels in dust from their household vacuum cleaners.

26 higher in POP III/IV compared to non-POP and POP I/II in the main in vivo loading direction; however,

27 d POP nanotraps, POP-Py, POP-pNH(2) -Py, and POP-oNH(2) -Py, have been designed and systematically ex

28 umannii and Pseudomonas aeruginosa (SNAP and POP studies).

29 or age at Tanner stages 2 or higher (2+) and POPs quartiles (Q1-4), adjusting for confounders (race/e

30 e contamination of metals (18 compounds) and POPs (43 compounds).

31 elucidated, but the effects of most COPs and POPs on inflammasome assembly have not been investigated

32 oteins encoding only a CARD or PYD, COPs and POPs, respectively, are assumed to inhibit inflammasome

33 rs associated with exposure to pathogens and POPs.

34 empirical studies for all Arctic species and POPs individually is unfeasible, in silico methods have

35 stigate the historical trends of atmospheric POPs in a region.

36 mpler and that spatial analysis of tree bark POPs concentrations can often pinpoint their sources.

37 A series of pyridine-based POP nanotraps, POP-Py, POP-pNH(2) -Py, and POP-oNH(2) -P

38 for the preparation of phosphabenzene-based POPs (Phos-POPs) under metal-free conditions is reported

39 as used to evaluate the relationship between POP levels in blood and dust, adjusting for child's age,

40 udies have investigated associations between POPs and LTL.

41 these results reveal important links between POPs and contrasting energetic pathways.

42 models indicated that relationships between POPs, trophic transfers, and traits were relatively well

43 gical evidence of the putative disruption by POPs of the adipose tissue oxidative microenvironment.

44 Risk-based analysis of several carcinogenic POPs indicated that the fish with the highest levels of

45 s a source of children's exposure to certain POPs.

46 lipophilic and readily adsorbs and collects POPs from the atmosphere.

47 mechanisms for a combination of three common POPs using a systems biology approach, which may link PO

48 higher than levels observed for conventional POPs detected in the samples.

49 des) to comprehensively assess their current POP concentrations and infer the potential sources of th

50 ponents, including posterior pharynx defect (POP-1)/TCF, APC related/adenomatosis polyposis coli (APR

51 Dietary POP levels differed significantly between treatments in

52 ing molecular mechanisms that link different POPs to common metabolic diseases.

53 the vertical distribution of truly dissolved POPs at two sites in the Atlantic Ocean.

54 (biological pump), as key processes driving POPs plankton phase concentrations in the global oceans.

55 ablished cohort, quantifying levels of eight POPs and four groups of oxidative stress biomarkers in a

56 anisms were analyzed for legacy and emerging POPs (polychlorinated biphenyls (PCBs), polybrominated d

57 e used to determine the state of equilibrium POPs reached in the passive samplers.

58 Contrary to expectation, POP concentrations did not demonstrate an associated dis

59 However, the association of low-exposure POPs with thyroid hormones (THs) remains unclear.

60 such, tree bark is an ideal sampler to find POPs sources globally, regionally, or locally.

61 For stream-resident fish, POP congener pattern was influenced by the presence of s

62 struction techniques and graft materials for POP treatment.

63 tion after the placement of vaginal mesh for POP repair or SUI surgery.

64 women who underwent transvaginal repair for POP or SUI with mesh between January 1, 2008, and Decemb

65 se inhibitors that were highly selective for POP over a number of homologous proteins.

66 ds) must be employed to inhibit FAP than for POP.

67 egetation is also an important reservoir for POPs.

68 The work provides promising results for POPs as an economical material for multiple environmenta

69 ne challenged with SAV as fry in freshwater (POP 1) and one challenged with SAV as post-smolts in sea

70 st resistance to PD in both populations (fry POP 1 h(2)~0.5; post-smolt POP 2 h(2)~0.4).

71 ork is needed to develop the next-generation POPs for practical applications.

72 tation; therefore, young cubs present higher POPs concentrations than their mothers.

73 in both the sire- and dam-based analyses in POP 1, and genome-wide significance in a combined analys

74 -wide significance in a combined analysis in POP 2.

75 modulus was lower and peak stretch higher in POP III/IV compared to non-POP and POP I/II in the main

76 portant to be able to predict variability in POP concentrations in changing environments.

77 r, and body size explained some variation in POP burdens between organisms.

78 erage concentrations as well as variation in POPs among individuals.

79 In conclusion, PS liquid margarine increased POP content in foods with a POP profile characterized by

80 total POP content by over 75% and individual POP content by over 50%.

81 ght important differences between individual POP members.

82 Of the four known POPs, only POP2 is reported to regulate NF-kappaB-depend

83 ed with metabolic diseases; three well-known POPs [2,3,7,8-tetrachlorodibenzodioxin (TCDD), 2,2 ,4,4

84 FA) and persistent organic pollutant levels (POPs).

85 g a systems biology approach, which may link POP exposure to diseases.

86 trends indicate that concentrations of many POPs (PCBs, DDT, HCHs, endosulfan) have declined signifi

87 Mean POP-SS at 1 year did not differ substantially between co

88 Mean POP-SS at 2 years were: standard 4.9 (SD 5.1) versus mes

89 The mean POP-SS score at 2 years was 3.2 (SD 3.4) in the interven

90 na from 12 locations worldwide, and measured POP levels using combined liquid or gas chromatography a

91 The noninvasive method for measuring POP concentrations in killer whales through scat employe

92 ontrol margarine resulted in a higher median POP content per food portion (1.35mg, range 0.08-13.20mg

93 onstrated that the extent of salmon-mediated POP transfer and uptake in Great Lakes tributaries is lo

94 tary sources, or bioaccumulate or metabolize POPs differently.

95 ions fell within a factor 6 of the monitored POP residues in biota.

96 Comparing our model results with monitored POP residues in biota revealed that, on average, all pre

97 Currents seemed more important in moving POPs to deeper water masses than the biological pump.

98 summary measure of exposure due to multiple POPs (environmental risk score or ERS).

99 A series of pyridine-based POP nanotraps, POP-Py, POP-pNH(2) -Py, and POP-oNH(2) -Py, have been de

100 stretch higher in POP III/IV compared to non-POP and POP I/II in the main in vivo loading direction;

101 at a high nuclear level, whereas low nuclear POP-1 promotes seam cell self-renewal.

102 end testosterone as a sensitive biomarker of POP exposure and that seasonal patterns are investigated

103 sed design and synthesis of a novel class of POP inhibitors based on hexahydroisoindoles.

104 Eight male foxes were given a diet of POP-contaminated minke whale blubber, whereas their eigh

105 To explore the nature and extent of POP biotransport by salmon, we compared 58 PCB and 6 PBD

106 The identification of POP opens up numerous avenues for continued scientific e

107 Predictive models of POP content versus storage time were established.

108 ugh providing more consistent predictions of POP bioaccumulation than steady-state models, variabilit

109 chanics change with onset and progression of POP.

110 analysis of K(SA), estimated as the ratio of POP concentrations in snow and air from previously repor

111 Here, we present an exhaustive sampling of POP with a known inhibitor, Z-pro-prolinal.

112 inding kinetics using both our own series of POP inhibitors and others' discovered hits.

113 for use in the pelvic floor for treatment of POP and SUI.

114 The combined use of POP mesh and SUI mesh sling was associated with the high

115 Bioaccumulation of POPs increased with age, with the exception of presumed

116 Svalbard when predicting bioaccumulation of POPs using the optimal modeling for ecotoxicological app

117 f trophic variability on biomagnification of POPs in Arctic food webs.

118 t serum concentrations of several classes of POPs (polybrominated diphenyl ethers [PBDEs], polychlori

119 rall mass, concentration, and composition of POPs in yellowfin and examined the differences in levels

120 ociations between maternal concentrations of POPs and offspring allergic sensitization at 20 years of

121 ons, differences in tissue concentrations of POPs between plastic ingestion subgroups, fugacity calcu

122 Concentrations of POPs detected in the North Atlantic near the surface (e.

123 othesized that high plasma concentrations of POPs in Asian Indian migrants are linked to a variety of

124 Higher concentrations of POPs in plasma are associated with reduced ALS survival,

125 Maternal concentrations of POPs were, however, positively associated with offspring

126 10-2013) were analyzed for concentrations of POPs.

127 nderstood amplification of concentrations of POPs.

128 ecimen to evaluate the thyroid disruption of POPs.

129 The spatial distribution of POPs indicated that the major sources in the region are

130 ody condition were not the primary driver of POPs in polar bears, but were controlled in large part b

131 We assessed the combined effect of POPs on oxidative stress/glutathione system biomarkers u

132 cterise and quantify the combined effects of POPs on ALS and supports the concept that environmental

133 t of predictive biomarkers of the effects of POPs, which could translate into disease prevention and

134 o understand potential obesogenic effects of POPs.

135 art by primary and/or secondary emissions of POPs.

136 to assess the association of low exposure of POPs, including polybrominated diphenyl ethers (PBDEs),

137 fication is relevant for diverse families of POPs, independent of their volatility.

138 ween the structural and chemical features of POPs and their adsorption capacities is discussed, mainl

139 tations and demonstrates the introduction of POPs recently listed under the Stockholm Convention into

140 are occupationally exposed to high levels of POPs.

141 ) provided plasma samples for measurement of POPs.

142 We assessed the underlying mechanisms of POPs that have been associated with metabolic diseases;

143 ollutants (POPs)) and a synthetic mixture of POPs, using GAL4-UAS-based in vitro luciferase reporter

144 commonly used to evaluate the performance of POPs for carbon capture, including CO2 capacity, enthalp

145 UNEP global convention for the regulation of POPs.

146 tterns indicated that salmon are a source of POPs to brook trout in stream reaches receiving salmon s

147 Transfer of POPs through mobilization of endogenous lipid stores dur

148 the analysis of long-term temporal trends of POPs in the African atmosphere.

149 Observed increasing trends of POPs in the tree-ring samples were representative for th

150 This study broadens the understanding of POPs in the endangered Southern Resident killer whale po

151 act as a passive sampler than as a vector of POPs, thus reflecting the POP profiles of simultaneously

152 in the development of prolyl oligopeptidase (POP) and fibroblast activation protein alpha (FAP) coval

153 ine peptidases of the prolyl oligopeptidase (POP) family are of substantial therapeutic importance be

154 Prolyl oligopeptidase (POP) is a large 80 kDa protease, which cleaves oligopept

155 vides tunable control of surface features on POPs, thereby affording control over bulk material prope

156 an simultaneously also enhance the opposing, POP-1 activity, suggesting a role in modulating the pote

157 ons with diabetes after adjustment for other POPs were strongest with the more volatile, non-dioxin-l

158 Concentrations of other POPs such as PCDD/Fs and PBDEs have not changed signific

159 Thus, unlike other POPs thought to diminish innate protection, POP2 reduces

160 ivity found that POP-oNH(2) -Py outperformed POP-pNH(2) -Py.

161 s, were strongly associated with the overall POP load.

162 -1) upon treatment with I(2) vapor, the 3D p-POP is the first member of a new class of permanently po

163 pai-conjugated porous organic polymer (3D p-POP) using catalyst-free Diels-Alder cycloaddition polym

164 er coordination with Ru species, a Ru/F-Phos-POPs catalyst exhibited high catalytic efficiency in the

165 ple, partially fluorinated Phos-POPs (F-Phos-POPs) were obtained with a surface area of up to 591 m(2

166 As an example, partially fluorinated Phos-POPs (F-Phos-POPs) were obtained with a surface area of

167 eparation of phosphabenzene-based POPs (Phos-POPs) under metal-free conditions is reported, without t

168 ations between persistent organic pollutant (POP) concentrations and body mass index (BMI).

169 BDE-209 in the persistent organic pollutant (POP) convention as well as the need for strategies to re

170 nships between persistent organic pollutant (POP) levels in the blood of children with leukemia and P

171 ling (EPS) of persistent organic pollutants (POP) in fish tissue has been hitherto limited to applica

172 on legacy persistent chlorinated pollutants (POPs), while the effects of poly- and perfluoroalkyl sub

173 rations of 18 persistent organic pollutants (POPs) and 9 toxic elements in blood, as well as total an

174 entrations of persistent organic pollutants (POPs) and mercury (Hg) in springtails from the field, an

175 tions between persistent organic pollutants (POPs) and metabolic diseases, but testable hypotheses re

176 cumulation of persistent organic pollutants (POPs) are critical for hazard and ecosystem health asses

177 Persistent organic pollutants (POPs) are developmental toxicants, but the impact of bot

178 y exposure to persistent organic pollutants (POPs) for 22 months.

179 e analysis of persistent organic pollutants (POPs) has the potential to characterize sources, sinks,

180 exposures to persistent organic pollutants (POPs) have been associated with asthma medication use an

181 and emerging persistent organic pollutants (POPs) have been reported in polar regions, and act as se

182 Concern about persistent organic pollutants (POPs) in Californians prompted the state's biomonitoring

183 as to examine persistent organic pollutants (POPs) in relation to pubertal onset.

184 occurrence of persistent organic pollutants (POPs) in the Arctic has been of constant concern, as the

185 stribution of persistent organic pollutants (POPs) in the deep ocean.

186 e a source of persistent organic pollutants (POPs) in the human diet.

187 ative role of persistent organic pollutants (POPs) in the induction of oxidative damage in cell struc

188 Exposure to persistent organic pollutants (POPs) is known to increase risk of diabetes.

189 l exposure to persistent organic pollutants (POPs) is limited by costs and logistics of follow-up.

190 Several persistent organic pollutants (POPs) like polycyclic aromatic hydrocarbons (PAHs), poly

191 asurements of persistent organic pollutants (POPs) near the North American Great Lakes-measurements t

192 vironmentally persistent organic pollutants (POPs) occurs through the diet, the host gastrointestinal

193 Exposure to persistent organic pollutants (POPs) such as dioxins, furans, and polychlorinated biphe

194 ng sources of persistent organic pollutants (POPs) to the atmosphere can sometimes be difficult.

195 contemporary persistent organic pollutants (POPs) to the local environment.

196 Convention on Persistent Organic Pollutants (POPs) was established to generate long-term data necessa

197 lled "legacy" persistent organic pollutants (POPs)) and a synthetic mixture of POPs, using GAL4-UAS-b

198 entrations of persistent organic pollutants (POPs), and evaluate risk factors associated with exposur

199 nification of persistent organic pollutants (POPs), but factors affecting their transfer through food

200 amples for 50 persistent organic pollutants (POPs), including 21 PCB congeners, 8 PBDE congeners, and

201 Persistent organic pollutants (POPs), specifically PCBs, PBDEs, and DDTs, in the marine

202 Persistent organic pollutants (POPs), such as dichlorodiphenyltrichloroethane (DDT) and

203 can transport persistent organic pollutants (POPs), such as polychlorinated biphenyls (PCBs) and poly

204 ndustrial-use Persistent Organic Pollutants (POPs), such as polychlorinated biphenyls (PCBs), have be

205 aminated with persistent organic pollutants (POPs).

206 such as some persistent organic pollutants (POPs).

207 anthropogenic-persistent organic pollutants (POPs).

208 ng effects of persistent organic pollutants (POPs).

209 any adsorbed persistent organic pollutants (POPs).

210 ral trends of persistent organic pollutants (POPs: PCBs, OH-PCBs, p, p'-DDE, HCB, beta-HCH, oxychlord

211 or metals and persistent organic pollutants, POPs) to map the bioavailable contamination level of fre

212 thiol functionalized porous organic polymer (POP) using simple free radical polymerization techniques

213 new porphyrin-based porous organic polymer (POP) with BET surface area ranging from 780 to 880 m(2)/

214 developed Programmable Order Polymerization (POP), Microfluidic Combinatorial Assembly of DNA (M-CAD)

215 The emergence of porous organic polymers (POPs) has provided great opportunities for new applicati

216 Porous organic polymers (POPs) have shown significant promise owing to their sele

217 the preparation of porous organic polymers (POPs) with task-specific functionalities has been exceed

218 terials, especially porous organic polymers (POPs), as one type of the most promising candidates for

219 apacity among known porous organic polymers (POPs).

220 of the first example of a polyoxopalladate (POP)-based metal-organic framework (MOF).

221 ucial for nectar spur development, POPOVICH (POP), which encodes a C2H2 zinc-finger transcription fac

222 tterns and use trait-based models to predict POP bioaccumulation.

223 The Pregnancy Outcome Prediction (POP) study was a prospective cohort study between Januar

224 The Pregnancy Outcome Prediction (POP) study was a prospective cohort study of nulliparous

225 trols from the Pregnancy Outcome Prediction (POP) study, conducted in Cambridge, UK, to identify pred

226 bility to reliably back-extrapolate prenatal POP levels from levels 9 years after delivery, with Supe

227 Plant sterol (PS) oxidation products (POP) derived from sitosterol and campesterol were measur

228 aldehyde and phytosterol oxidation products (POPs) were evaluated as oxidative markers.

229 roduction of phytosterol oxidation products (POPs).

230 ic and oleic acid) and triglyceride profile (POP, SOS and POS) to cocoa butter.

231 ncontinence (SUI) and pelvic organ prolapse (POP) have produced highly variable outcomes, causing lif

232 aft, has been used in pelvic organ prolapse (POP) repair and stress urinary incontinence (SUI) to aug

233 l function may induce pelvic organ prolapse (POP).

234 ting the role of PYRIN domain-only proteins (POPs) and the related CARD-only proteins (COPs) in regul

235 Pyrin domain-only proteins (POPs) are recently evolved, primate-specific proteins de

236 ammasome, namely pyrin domain-only proteins (POPs), caspase activation recruitment domain (CARD)-only

237 ies of pyridine-based POP nanotraps, POP-Py, POP-pNH(2) -Py, and POP-oNH(2) -Py, have been designed a

238 s a critical and in-depth analysis of recent POP research as it pertains to carbon capture.

239 ations in snowmelt due to snowpack releasing POPs to seawater.

240 Thereby, RNT-1/BRO-1 appears to render POP-1 below the level required for its repressor functio

241 The resulting POP is able to remove aqueous and airborne mercury with

242 .e. the Pelvic Organ Prolapse Symptom Score [POP-SS]) and condition-specific (ie, prolapse-related) q

243 mptoms (Pelvic Organ Prolapse Symptom Score [POP-SS]) at 2 years.

244 The SEROCoV-POP study is a population-based study of former particip

245 tudinal study of puberty in girls with serum POPs measurements (to our knowledge) reveals a delay in

246 xamined the differences in levels of several POP congeners of potential relevance to human health.

247 ernal and paternal concentrations of several POPs were associated with statistically significant diff

248 172 and 195) serum concentrations of several POPs were statistically associated with lower birth weig

249 steady state bioaccumulation models simplify POP bioaccumulation dynamics, assuming that pollutant up

250 populations (fry POP 1 h(2)~0.5; post-smolt POP 2 h(2)~0.4).

251 but different major TAGs (PPO-, PSO-, SSO-, POP- and SOS-rich blends) were evaluated.

252 mospheric transport potential of the studied POPs.

253 thout mesh but concurrent sling use for SUI (POP sling group), and sling for SUI alone (SUI sling gro

254 We created three summed POP metrics based on toxic equivalency factor (TEF), a p

255 ltidimensional scaling (NMDS), we found that POP congener patterns of Pacific salmon varied among reg

256 trap regeneration and selectivity found that POP-oNH(2) -Py outperformed POP-pNH(2) -Py.

257 Our results indicate that POP exposure may enhance alternative pathways to the glu

258 Single-crystal X-ray analysis indicated that POP-oNH(2) -Py provided a stronger complex compared to P

259 athways in mothers and cubs, indicating that POP exposure alters the energy metabolism, which, in tur

260 of endogenous pop-1, support the model that POP-1(TCF) induces differentiation at a high nuclear lev

261 rdens), contrasting traditional beliefs that POPs do not reach the deep ocean.

262 These results indicate that POPs at low levels might be related to reduced THs.

263 Recent studies suggest that POPs affect the lipid metabolism in female polar bears;

264 lmars from Norwegian waters and compared the POP concentrations in their liver and muscle tissue with

265 cation influences, and may even control, the POP occurrence in cold environments.

266 Parameter values were obtained from the POP study, and costs were mainly obtained from the Engli

267 we identified homologs of this enzyme in the POP family and confirmed the presence of carboxypeptidas

268 proliferative activity of palbociclib in the POP trial (P = .005).

269 r and fall, while mean concentrations of the POP chlordane (SigmaCHL) were lower for land-based bears

270 All of the POP nanotraps demonstrated record uptakes and rapid capt

271 Further testing on the POP nanotrap regeneration and selectivity found that POP

272 han as a vector of POPs, thus reflecting the POP profiles of simultaneously ingested prey.

273 w, representative recent developments in the POPs-based catalysts with hierarchically porous structur

274 alyses revealed that the distribution of the POPs was not only driven by the feeding traits of the sp

275 tion to identify common mechanisms for these POPs within two or fewer interaction steps downstream of

276 ational estimates of contamination for these POPs.

277 ies into underlying mechanisms by which this POP mixture could produce or exacerbate metabolic diseas

278 explore associations between adipose tissue POP concentrations and the in situ oxidative microenviro

279 -Py provided a stronger complex compared to POP-pNH(2) -Py owing to the intramolecular hydrogen bond

280 and negatively, respectively, correlated to POP exposure, whereas in cubs, 2585 positively and 1690

281 Due to POP's size and to the buried nature of its active site,

282 l gut microbiota are likely to be exposed to POPs.

283 Our data indicate that prenatal exposure to POPs appears to be associated with airway obstruction bu

284 Here, we hypothesized that exposure to POPs differentially alters genome-wide gene transcriptio

285 sing the level and risk of human exposure to POPs through ingestion of wild fish.

286 e associations between prenatal exposures to POPs and allergic sensitization and lung function in 20-

287 Total POP contents followed the order MPS>>FJPS>MFJPS.

288 These models explain total POP content by over 75% and individual POP content by ov

289 Females transfer POPs to their offspring through gestation and lactation;

290 vaginal mesh plus sling group), transvaginal POP repair with mesh and no concurrent sling use (vagina

291 sling use (vaginal mesh group), transvaginal POP repair without mesh but concurrent sling use for SUI

292 ups based on the amount of mesh transvaginal POP repair surgery with mesh and concurrent sling use (v

293 upper incisor, and the occlusal plane (UOP, POP) were significantly correlated with post-treatment.

294 atal surface angle) and occlusal planes (UOP/POP) were significantly correlated with the difference i

295 Finally, a concise outlook for utilizing POPs for carbon capture is discussed, noting areas in wh

296 lenged with SAV as post-smolts in sea water (POP 2).

297 ptional activation through interactions with POP-1/Tcf.

298 mechanical changes may occur in the USL with POP onset and progression.

299 lusion, we have identified a new type within POP enzymes that exhibits not only unique activity but a

300 SL in post-menopausal women with and without POP at various stages.