ライフサイエンスコーパス: organic chemical

1 cient to prevent the biomagnification of any organic chemical.

2 ish describing the uptake and disposition of organic chemicals.

3 lculate the Globally Balanced State (GBS) of organic chemicals.

4 -term cumulative exposure to metals and some organic chemicals.

5 edict partition coefficients (K) for neutral organic chemicals.

6 s, methane, and other valuable inorganic and organic chemicals.

7 riod of time while avoiding the use of toxic organic chemicals.

8 s proxies for the broad class of hydrophobic organic chemicals.

9 ential oil composed of volatile, hydrophobic organic chemicals.

10 ls and shallow groundwater contaminated with organic chemicals.

11 e descriptors accurately and quickly for new organic chemicals.

12 gement to protect aquatic ecosystems against organic chemicals.

13 s using pooled human plasma spiked with >400 organic chemicals.

14 been applied to a large number of ionizable organic chemicals.

15 rations of salts, alkaline earth metals, and organic chemicals.

16 ffect the environmental fate of semivolatile organic chemicals.

17 presence of EPFRs in regulating the fate of organic chemicals.

18 ant role in environmental risk assessment of organic chemicals.

19 rcotic toxicity and the chemical activity of organic chemicals.

20 that address the approval and regulation of organic chemicals.

21 process for bioaccumulation of many neutral organic chemicals.

22 forces that govern the environmental fate of organic chemicals.

23 enough to control the global distribution of organic chemicals.

24 inc, cadmium, lead, mercury, and nickel) and organic chemicals (a phthalate and a number of polynucle

25 shown to be important reservoirs for neutral organic chemicals across a wide range of partitioning pr

26 Emphasis of the space upon organic chemicals after 1830 prompted the recognition of

27 ed here can be expanded to produce important organic chemicals, all through biological activation of

28 State-of-the-art organic chemical analysis instruments can perform valuab

29 ing using a rotating drum impactor (RDI) and organic chemical analysis using direct liquid extraction

30 We comprehensively analyzed exogenous organic chemicals and associated metabolites in ten seme

31 risks depend on the bioavailable fraction of organic chemicals and cannot be comprehended by their to

32 ticular for solar-energy-driven synthesis of organic chemicals and commodities, moving away from simp

33 even of the most widely used tire-associated organic chemicals and four of their degradation products

34 -necrosis require incremental amounts of the organic chemicals and increased levels of oxidative stre

35 test danger because of their high content of organic chemicals and prooxidative potential.

36 For organic chemicals and radiation, the odds ratios for bot

37 iptors for numerous environmentally relevant organic chemicals and system parameters for environmenta

38 ng by touch,(2) reflected light,(3) volatile organic chemicals, and root exudates.(4)(,)(5) The impor

39 ecies sensitivity among different classes of organic chemicals, and the reported results herein have

40 The hydrolysis rates of many organic chemicals are accelerated under alkaline conditi

41 Several kilometers downhole, these organic chemicals are exposed to temperatures up to 200

42 aerobic biodegradation rates (half-lives) of organic chemicals are pivotal for environmental risk ass

43 Hundreds of organic chemicals are used during natural gas extraction

44 The method is applied to 180 organic chemicals as a case study.

45 Initially, SHEDS-HT has been applied to 2507 organic chemicals associated with consumer products and

46 tool to track the in situ transformation of organic chemicals at contaminated sites.

47 t human-equivalent PODs for oral exposure to organic chemicals based on chemical structure.

48 uding endocrine disruptors and inorganic and organic chemicals based on gene expression.

49 tates the in situ measurement of hydrophobic organic chemicals bioavailability in sediments in terms

50 o has the potential to enhance regulation of organic chemicals by linking results from laboratory tes

51 The uptake of organic chemicals by plants is considered of great signi

52 retrospective risk assessment frameworks for organic chemicals; by doing so, realistic decision-makin

53 hat membrane-water partition coefficients of organic chemicals can be used to predict bioaccumulation

54 Organic chemicals can contribute to local and regional l

55 air partitioning, particularly for ionizable organic chemicals compared to nonionizable ones, challen

56 Ascorbic acid (AA) is a highly water-soluble organic chemical compound and plays a significant role i

57 Many mammals rely on volatile organic chemical compounds (VOCs) produced by bacteria f

58 ntial TH disruptive contaminants (metals and organic chemical compounds) affect plasma TH levels in f

59 actions of, and biodegradation pathways for, organic chemical compounds, especially those produced by

60 ) models of the distribution of nonionizing, organic chemical concentrations in indoor environments r

61 on to corn resulted in measurable effects on organic-chemical concentrations in rain-induced agricult

62 s are the main sources of pollution for most organic chemicals considered, but north of the Arctic ci

63 The approach is applicable to nonpolar organic chemicals containing C, H, F, Cl, Br, and I, hav

64 k soldier fly) analyzing a large spectrum of organic chemical contaminants, including pesticides (n =

65 lic aromatic hydrocarbons (PAHs), a group of organic chemical contaminants.

66 Results document substantial and varying organic-chemical contribution to surface water from effl

67 ntrations of metals (especially cadmium) and organic chemicals correlated with the presence of tumor

68 enhanced inorganic chemical remediation and organic chemical degradation using various pathway-engin

69 quently release free radicals and accelerate organic chemical degradation.

70 Numerous organic-chemical detections per site (median number of c

71 es' life cycle ecotoxicity effect related to organic chemical emissions.

72 genic Volatile Organic Compounds (BVOCs) are organic chemicals emitted primarily by flora.

73 Biodegradation of organic chemicals emitted to the environment is carried

74 chondrites because of their implications for organic chemical evolution and the origin of life.

75 are indicative of an asymmetric influence on organic chemical evolution before the origin of life.

76 y addresses the question whether hydrophobic organic chemicals exerting no toxicity at their solubili

77 We demonstrate that organic chemicals extracted from DEP induce oxidative st

78 However, organic chemical fate regulated by EPFRs has rarely been

79 Screening organic chemicals for hazard and risk to human health re

80 (BAC), applied as pretreatments to mitigate organic chemical fouling of reverse osmosis (RO) membran

81 pathways are most likely to be relevant for organic chemicals found in the natural environment.

82 method for assessing and studying release of organic chemicals from a polymeric matrix is well suited

83 ed for the extraction of complex mixtures of organic chemicals from lipid-rich biota.

84 potential for bioaccumulation of persistent organic chemicals from sediment useful to prioritize man

85 f the most important elimination pathways of organic chemicals from the environment.

86 Equilibrium partition coefficients of organic chemicals from water to an organism or its tissu

87 In Pennsylvania, two organic chemicals/groups had reduced odds of detection w

88 Diphenylcyclopropenone (DPC) is an organic chemical hapten which induces allergic contact d

89 of soil and aquatic systems by inorganic and organic chemicals has become a global concern.

90 Partitioning behavior of organic chemicals has tremendous influences on their env

91 Numerous polar anthropogenic organic chemicals have been found in the aqueous environ

92 changes in catalysts and controls of flow of organic chemicals have evolved in the divided space of c

93 was applied to determine the toxicity of 35 organic chemicals, having a wide range of toxicity to fi

94 mass balance model was developed to estimate organic chemical HLB from measured HLT data in mammals.

95 three different AC treatments on hydrophobic organic chemical (HOC) concentrations in pore water, ben

96 oplastic will transfer hazardous hydrophobic organic chemicals (HOC) to marine animals' has been cent

97 ish tests, sorption of 11 highly hydrophobic organic chemicals (HOCs) (log KOW 5.5-7.8) from differen

98 e environmental chemodynamics of hydrophobic organic chemicals (HOCs) are often rate-limited by diffu

99 ly applied for the enrichment of hydrophobic organic chemicals (HOCs) from various types of samples a

100 The binding and speciation of hydrophobic organic chemicals (HOCs) in aqueous solutions were deter

101 ecological health risks posed by hydrophobic organic chemicals (HOCs) in sediments and soils.

102 ibe bioaccumulation potential of hydrophobic organic chemicals (HOCs) in temperate aquatic food webs,

103 nsport, and fate of semivolatile hydrophobic organic chemicals (HOCs) in the environment.

104 o-water fluxes of sediment-bound hydrophobic organic chemicals (HOCs) in the presence of bioturbators

105 For hydrophobic organic chemicals (HOCs) such techniques can lead to und

106 ssolved concentration (Cfree) of hydrophobic organic chemicals (HOCs), leading to poorly defined expo

107 solved aqueous concentrations of hydrophobic organic chemicals (HOCs), such as polycyclic aromatic hy

108 quantitative determination of BPA and other organic chemicals (i.e., benzophenone-3, triclosan, para

109 source or sink for all or specific groups of organic chemicals in a small river.

110 d melt processes on the fate of semivolatile organic chemicals in a temperate Alpine glacier.

111 effects of temperature changes on the TK of organic chemicals in aquatic ecosystems.

112 implications for the toxicokinetics (TK) of organic chemicals in aquatic organisms.

113 sess aerobic and anaerobic transformation of organic chemicals in aquatic sediment systems and is an

114 tive for separating and quantifying nonpolar organic chemicals in complex mixtures.

115 ally balanced bioaccumulation (3B) model for organic chemicals in fish.

116 Widespread use of organic chemicals in household and personal care product

117 s about whether concentrations of persistent organic chemicals in human milk decrease over the course

118 echanisms and kinetics of the degradation of organic chemicals in hydraulic fracturing fluids.

119 pproach to include occupational exposures to organic chemicals in life cycle impact assessment (LCIA)

120 olved concentration (C(free)) of hydrophobic organic chemicals in sediments and soils is considered t

121 The bioavailability of organic chemicals in soil and sediment is an important a

122 tivity, hazards, and risks of six classes of organic chemicals in the aquatic environment.

123 1) lw, representing a dynamic stock of toxic organic chemicals in the study area.

124 pids, were used to predict concentrations of organic chemicals in two fish species: rainbow trout (On

125 characterize the equilibrium partitioning of organic chemicals in various environmental and technical

126 3032 measurement end points for 477 discrete organic chemicals including 964 half-lives, 1199 AEs and

127 flowing river water that was spiked with 22 organic chemicals including pharmaceuticals, pesticides

128 Polar organic chemical integrative sampler (POCIS) is a passiv

129 Modeling and prediction of polar organic chemical integrative sampler (POCIS) sampling ra

130 The sampler is based on a modified Polar Organic Chemical Integrative Sampler (POCIS) with a weak

131 ompare the conventional pharmaceutical polar organic chemical integrative sampler (POCIS) with modifi

132 te sorbent material (e.g., in a POCIS; polar organic chemical integrative sampler) or to reduce the s

133 ique OMPs for target quantification in polar organic chemical integrative samplers (POCIS) and grab s

134 me-weighted grab samples and companion polar organic chemical integrative samplers (POCIS) collected

135 the boundary layer compared to that of polar organic chemical integrative samplers (POCIS) deployed s

136 e fathead minnows, freshwater mussels, polar organic chemical integrative samplers (POCIS), and polye

137 The extracts, derived from polar organic chemical integrative samplers (POCIS), were anal

138 ling as well as passive sampling using polar organic chemical integrative samplers (POCIS).

139 samplers and hydrophilic compounds in polar organic chemical integrative samplers.

140 nd natural oxidants-that transform precursor organic chemicals into OM remain unclear.

141 t in the abiotic oxidative transformation of organic chemicals into OM, while dissolved oxygen (DO) i

142 tant compartments in partitioning of neutral organic chemicals into organisms.

143 Uptake and effects of ionizable organic chemicals (IOCs) that are weak acids in aqueous

144 (pesticides and pharmaceuticals), and other organic chemicals known or suspected to pose environment

145 ver-expanding, structurally varied series of organic chemical libraries.

146 their respective protein products, and other organic chemicals made by the cell create these signpost

147 was done using monitoring data of biota and organic chemicals, mainly pesticides, from five studies

148 addition step and the use of requisite small organic chemical matrixes from MALDI.

149 ere found on independent datasets of neutral organic chemicals (measured log K(ow) 3.3-6.2).

150 y-polycyclic aromatic hydrocarbons, volatile organic chemical metabolites, metals/metalloids, levoglu

151 luminescent regarding the detection of small organic chemicals, metal ions and biomarkers.

152 ogonally reactive groups were synthesized by organic-chemical methods.

153 interactions between environmental materials-organic chemicals, minerals, and natural oxidants-that t

154 ead environmental pollution by inorganic and organic chemicals, novel methods of decontamination and

155 Production of organic chemicals (OCs) is increasing exponentially, and

156 our knowledge, the first risk assessment of organic chemicals on the continental scale comprising 4,

157 plied successfully to a diversity of neutral organic chemicals, only the RT-S9 assay has been applied

158 ovides new insights into the partitioning of organic chemicals onto biofilms and shows clear linkages

159 despite the presence of heavy metals, other organic chemicals or dissolved organic matter.

160 The discharge of persistent and mobile organic chemicals (PMOCs) into the aquatic environment i

161 This study aimed to examine organic chemical pollutants in seminal plasma, including

162 mical processes, including biodegradation of organic chemical pollutants.

163 tigated the mechanism by which redox cycling organic chemicals, prepared from DEP, induce phase II en

164 se biocatalysts can significantly accelerate organic chemical processes and improve product stereospe

165 ectrochemical reduction of carbon dioxide to organic chemicals provides a value-added route for mitig

166 cific enhancement of the reaction rate of an organic chemical reaction can be observed.

167 ely, can be understood in terms of classical organic chemical reaction pathways.

168 sults, which can be rationalized in terms of organic-chemical reaction mechanisms and density-functio

169 Networks of organic chemical reactions are important in life and pro

170 ate solvated electrons for driving reductive organic chemical reactions in a quantifiable and control

171 As some of the oldest organic chemical reactions known, the ionic additions of

172 ies of a chemical "space" comprising 81,000+ organic chemicals registered in regulatory and academic

173 Humans are exposed to organic chemicals released to indoor air through near-fi

174 In air-breathing organisms, an organic chemical's susceptibility to elimination via uri

175 our worked and impact intensities for 19,069 organic chemical/sector combinations with confidence int

176 ve been fabricated and evaluated as volatile organic chemical sensors.

177 d biphenyl compounds (PCBs) are highly toxic organic chemicals still prevalent in the environment.

178 In this regard, the use of certain organic chemicals such as dimethyl sulfoxide, polyethyle

179 ies used to assess the environmental fate of organic chemicals such as pesticides fail to replicate e

180 ly reduce the bioavailability of hydrophobic organic chemicals such as polychlorinated biphenyls (PCB

181 the addition of small quantities of certain organic chemicals, such as dimethylsulfoxide (DMSO), bet

182 Fluorinated organic chemicals, such as per- and polyfluorinated alky

183 Effective modeling of semivolatile organic chemical (SVOC) partitioning between air and ind

184 Many semivolatile organic chemicals (SVOCs) are ubiquitous in indoor envir

185 tors (EFs) for a broad range of semivolatile organic chemicals (SVOCs) from subtropical eucalypt fore

186 se dust extracts and a suite of semivolatile organic chemicals (SVOCs) that are often ubiquitously de

187 an important source of various semivolatile organic chemicals (SVOCs) to the atmosphere including po

188 ent-fluid compositions, varieties of abiotic organic chemical synthesis and extremophile microorganis

189 so in artificial molecular motors created by organic chemical synthesis(9-12).

190 lar oxygen is the quintessential oxidant for organic chemical synthesis, but many challenges continue

191 es the power of rhodium carbene chemistry in organic chemical synthesis.

192 1,4-Dioxane is a persistent and mobile organic chemical that has been found by the United State

193 uoroalkyl substances (PFASs) are fluorinated organic chemicals that are concerning due to their envir

194 xpand by orders of magnitude the coverage of organic chemicals that can be evaluated for their human

195 Diesel exhaust particles (DEP) contain organic chemicals that contribute to the adverse health

196 xhaust particles (DEP) contain redox cycling organic chemicals that induce pro-oxidative and pro-infl

197 To aid in molecular modeling, the use of organic chemicals that mimic key structures of the antag

198 On exposure to various volatile organic chemicals, the structures rapidly swell and unde

199 sediment pollution by persistent hydrophobic organic chemicals to bioaccumulation.

200 d a wide range of aquatic animal species and organic chemicals to quantify how temperature influences

201 ortance of glaciers as a secondary source of organic chemicals to remote aquatic ecosystems.

202 d to unravel the contribution of hydrophobic organic chemicals to sediment ecotoxicity.

203 arrier, producing increased accessibility of organic chemicals to the central nervous system; and nit

204 ated for over 35 days for nutrient and trace organic chemical (TOrC) removal from municipal wastewate

205 e most important and recognizable classes of organic chemical transformation.

206 d) (PLA) to clean H(2) fuel and a variety of organic chemicals under alkaline aqueous conditions.

207 of such a library for abiotic hydrolysis of organic chemicals under environmentally relevant conditi

208 ) designed to simulate the uptake of neutral organic chemicals under variable temperatures, external

209 ver, detailed understanding of the processes organic chemicals undergo in a glacial system was missin

210 rs (LCMs) are biphenyl- or cyclohexane-based organic chemicals used in electronic digital displays, a

211 Characterization of organic chemicals used in hydraulic fracturing and their

212 onitor and evaluate the fate and exposure of organic chemicals used indoors.

213 dioxide (CO(2)) can be converted to valuable organic chemicals using light irradiation and photocatal

214 role of the fish intestine as a barrier for organic chemicals using the epithelial barrier model bui

215 For instance, metal organic chemical vapor deposition (MOCVD) emerged in the

216 e alloy, Ga(Sbx)N1-x is synthesized by metal organic chemical vapor deposition (MOCVD) for solar hydr

217 e, we investigate the use of few-layer metal organic chemical vapor deposition (MOCVD) grown BN as a

218 low-melting, thermally stable cadmium metal-organic chemical vapor deposition (MOCVD) precursors hav

219 than those of conventional solid zinc metal-organic chemical vapor deposition (MOCVD) precursors.

220 synthesized via an industry-compatible metal-organic chemical vapor deposition (MOCVD) process.

221 gO(100) substrates at 410 degrees C by metal-organic chemical vapor deposition (MOCVD), and their pha

222 sced 2D WSe(2) films with Re atoms via metal-organic chemical vapor deposition is reported.

223 Specifically, a pulsed metal-organic chemical vapor deposition process is developed,

224 yer MoS(2) and WS(2) films grown using metal-organic chemical vapor deposition process.

225 atomic layer deposition) and MOCVD (= metal-organic chemical vapor deposition) processes in material

226 to AlN, grown on a c-plane sapphire by metal-organic chemical vapor deposition, using synchrotron rad

227 Se/MoSe(2)/ZnSe heterostructures using metal-organic chemical vapor deposition.

228 mechanism in GaN epilayers prepared by metal-organic chemical vapor deposition.

229 top electrode of a standard QCM using metal-organic chemical-vapor deposition (MOCVD).

230 Here we demonstrate the use of metal-organic chemical vapour deposition (MOCVD) and appropria

231 We designed a metal-organic chemical vapour deposition reactor to separate t

232 They are grown with a newly developed, metal-organic chemical vapour deposition technique, and show h

233 ction of WSe(2) on c-plane sapphire by metal-organic chemical vapour deposition.

234 single quantum well structure grown by metal organic chemical vapour deposition.

235 Plastic losses can form volatile organic chemicals via photo-degradation and pose non-neg

236 The use of measured volatile organic chemical (VOC) concentrations in indoor air to e

237 ystem designed to determine complex volatile organic chemical (VOC) mixtures encountered in indoor wo

238 oot herbivory change the profile of volatile organic chemicals (VOCs) emitted by the host plant; (3)

239 Board (CARB) uses to determine how volatile organic chemicals (VOCs) from consumer products affect s

240 I) model, describing vapor entry of volatile organic chemicals (VOCs) into buildings located on conta

241 The hazard of organic chemicals was closely related to their physicoch

242 Organic chemicals were likely to exert acute lethal and

243 er partition coefficients (K(pw)) of neutral organic chemicals were measured using muscle proteins (f

244 Natural polyphenols are organic chemicals which contain phenol units in their st

245 ns, often generates a wide range of valuable organic chemicals which find applications in the pharmac

246 nt sink that forests provide for atmospheric organic chemicals which should be considered for emissio

247 nment are frequently exposed to a variety of organic chemicals, while these biological species may sh

248 oroalkyl acids (PFAAs), a group of synthetic organic chemicals with industrial and commercial uses, a

249 elative change in total mass for hydrophobic organic chemicals with log air-water partition coefficie

250 es C in boiling point, (3) a mixture of five organic chemicals with varying degrees of polarity, and