ライフサイエンスコーパス: cadmium

1 ance of this repression in cell tolerance to cadmium.

2 and gamma-glutamylcysteine, upon exposure to cadmium.

3 0.28 microg/L (95% CI: 0.27, 0.30) for urine cadmium.

4 o, i.e., hydrogen chalcogenide gas and alkyl cadmium.

5 20-40min following exposure to 3microgml(-1) cadmium.

6 tal concentrations of 0.303+/-0.035mg/kg for cadmium, 1.228+/-0.146mg/kg for lead and 0.094+/-0.013mg

7 lution species in the growth solution of the cadmium 2-ethylimidazolate metal-organic framework CdIF-

8 spectrometry to identify preformed, complex, cadmium 2-ethylimidazole containing solution species in

9 nine sulfur's presence makes the toxic metal cadmium a preferred substrate.

10 In vitro and animal data suggest that cadmium, a heavy metal that contaminates some foods and

11 UV, cells turned out to be more sensitive to cadmium, a priority pollutant widely disseminated in soi

12 e study demonstrates the complex behavior of cadmium accumulated by M. australiense and improves our

13 through leaf petioles; however, 8-fold more cadmium accumulated in PEI QD-treated leaves than in tho

14 This Ala391-associated cadmium accumulation also increased the phosphorylation

15 substitution has an effect on intracellular cadmium accumulation and cell toxicity, providing a pote

16 yase (smCSE) mineralizes CdS from an aqueous cadmium acetate solution via reactive H2S generation fro

17 Within this range of concentrations, cadmium affected only temporarily the electroactive biof

18 The gills did not become saturated with cadmium after 14 days of exposure and demonstrated a gre

19 Three treatments consisting of cadmium alone, zinc alone, and a mixture of cadmium and

20 important binary tellurides-polycrystalline cadmium and bismuth tellurides- were studied over the pH

21 as no consistent association between urinary cadmium and breast cancer mortality in the cohort studie

22 d not observe an association between urinary cadmium and breast cancer risk in any subgroup examined,

23 cess, and other chalcophilic metals (copper, cadmium and cobalt) were removed (as sulfides) in the st

24 the precision of the method for analysis of cadmium and copper ions (5.0 mug of each target ions, N=

25 cessfully applied for trace determination of cadmium and copper ions in food samples.

26 bon were found to be 145 and 95 mg g(-1) for cadmium and copper ions, respectively.

27 are 0.04 and 0.09 ng mL(-1) for the ions of cadmium and copper respectively, and the precision of th

28 rence study with other metal ions like lead, cadmium and copper showed a negligible change in fluores

29 lso functions in abiotic stress responses to cadmium and indole-3-butyric acid (IBA)-mediated auxin h

30 Cadmium and lead are ubiquitous environmental contaminan

31 Although some design rules from studies of cadmium and lead containing quantum dots can be applied,

32 , the presence of toxic heavy metals such as cadmium and lead in some of the most mature nanocrystals

33 concentration factor was 299.3 and 137.1 for cadmium and lead ions, respectively.

34 ed using an automatic mercury analyzer while cadmium and lead levels were determined by flame atomic

35 Cadmium and lead values in some samples were found highe

36 The concentrations of aluminium, arsenic, cadmium and lead were low, with mean concentrations of 1

37 In contrast, estimated dietary intake of cadmium and lead were not significantly associated with

38 In contrast, estimated dietary intake of cadmium and lead were not significantly associated with

39 In our case, cadmium and lead-induced genetic response systems in bac

40 loci 6q14.1 and 3q26.32 were associated with cadmium and mercury levels (P = 1.4 x 10(-10), beta = -1

41 Regardless of electrode, cadmium and nickel removal efficiencies were higher at p

42 nd trialkyl phosphine selenide by binding to cadmium and preventing the activation of trialkyl phosph

43 lly significant associations between dietary cadmium and risk of any of these cancers after adjustmen

44 nvironmental exposures to lead, mercury, and cadmium and the risk of hearing loss in adults and adole

45 cadmium alone, zinc alone, and a mixture of cadmium and zinc were used to determine the differences

46 highest concentrations of metals (especially cadmium) and organic chemicals correlated with the prese

47 0.44 microg/L (95% CI: 0.42, 0.47) for blood cadmium, and 0.28 microg/L (95% CI: 0.27, 0.30) for urin

48 01 to 0.45 with an average value of 0.34 for cadmium, and from <0.01 to 1.44 with an average value of

49 ifferent mechanisms of action for copper and cadmium, and highlight that mechanistic understanding of

50 Twentieth century zinc, cadmium, and lead concentrations are dominated by emissi

51 tative adsorption of cobalt, nickel, copper, cadmium, and lead ions.

52 rfjord in western Norway) for mercury, zinc, cadmium, and lead.

53 ns such as wounding or exposure to salinity, cadmium, and low temperature, thus validating the outcom

54 Genes with possible contribution to zinc, cadmium, and nickel hyperaccumulation and hypertolerance

55 tal tolerance and leaf accumulation of zinc, cadmium, and nickel.

56 Lead and cadmium are frequently encountered heavy metals in indus

57 -fluvalinate), then trace metals/metalloids (cadmium, arsenic), followed by the fungicide propiconazo

58 48 to 720 hours (summer worker lifespan) for cadmium, as the most time-dependent chemical as driven b

59 further evidence of physiological impacts of cadmium at environmental levels and might provide insigh

60 In this study, a multiplex cadmium biosensing construct was assembled by cloning a

61 uct was assembled by cloning a single-output cadmium biosensor element, cadRgfp, and a constitutively

62 The multiplex cadmium biosensors were responsive to cadmium concentrat

63 Biomarker data (blood cadmium, blood lead, blood mercury, urinary total arseni

64 The samples were analysed for lead and cadmium by a graphite furnace atomic absorption spectrom

65 straliense may process zinc much faster than cadmium by internally transporting the accumulated zinc

66 metal following accumulation from waterborne cadmium by the freshwater decapod crustacean Macrobrachi

67 Without oleic acid impurities, cadmium carboxylate can be completely displaced from the

68 The cadmium-carboxylate derivative is determined to have the

69 r electroanalysis using the determination of cadmium (Cd(2+)) by anodic stripping voltammetry (ASV).

70 transformed with OsPCS2a exhibited increased cadmium (Cd) and arsenic (As) tolerance and accumulation

71 Total mercury (Hg), cadmium (Cd) and lead (Pb) concentrations were determine

72 Long-term exposure to the heavy metals cadmium (Cd) and mercury (Hg) is known to increase the r

73 on, resistance to interfering metals such as cadmium (Cd) and zinc (Zn), and stable response in natur

74 ercury (Hg), Arsenic (As), Chromium (Cr) and Cadmium (Cd) are considered to be highly toxic and hazar

75 significant (p < 0.05) increase in cellular cadmium (Cd) concentration at 24 h (306 +/- 192 mg/L) as

76 Environmental cadmium (Cd) exposure is associated with type 2 diabetes

77 transporter mutant, opt3-2, over-accumulates cadmium (Cd) in seeds and roots but, unexpectedly, under

78 long-term increases in the concentration of cadmium (Cd) in soils.

79 Cadmium (Cd) is a toxic metal.

80 Cadmium (Cd) is an important environmental pollutant and

81 sis of radish roots exposed to lead (Pb) and cadmium (Cd) stresses has been performed using gas chrom

82 In this species, cadmium (Cd) tolerance seems to be constitutive, and the

83 rum (L. plantarum) strains in alleviation of cadmium (Cd) toxicity in vivo and demonstrated that the

84 uding mercury (Hg), arsenic (As), lead (Pb), cadmium (Cd), and chromium (Cr), from primary anthropoge

85 Limited data suggest that lead (Pb), cadmium (Cd), and uranium (U) may disrupt vitamin D meta

86 zinc (Zn), chromium (Cr)) and heavy metals (cadmium (Cd), lead (Pb) and nickel (Ni)) in some tubers,

87 adiation in combination with the heavy metal cadmium (Cd), using the MIXTOX approach.

88 al model and is known for its sensitivity to cadmium (Cd).

89 lerance of excess copper (Cu), zinc (Zn) and cadmium (Cd).

90 tration, and toxic sensitivity to waterborne cadmium (Cd).

91 In this work, we showed that cadmium [Cd(II)], a known human carcinogen, inhibited al

92 a series of partially and completely hollow cadmium chalcogenide nanoarchitectures with unprecedente

93 oieties that strongly bind to the surface of cadmium chalcogenide QDs.

94 roved photoluminescence (PL) line widths for cadmium chalcogenide-based nanocrystals.

95 Cadmium chalcogenides nanoplatelets (NPLs) strongly rely

96 le chalcogenidocadmates, a molecular form of cadmium chalcogenides with unprecedented one-dimensional

97 subcutaneously administered a combination of cadmium chloride (CdCl2) and methylmercury (II) chloride

98 nds to amino acid limitation and exposure to cadmium chloride (CdCl2) and sodium arsenite (NaAsO2).

99 ecreasing the L-type Ca current (with 50 mum cadmium chloride).

100 moval efficiencies for five metals (arsenic, cadmium, chromium, lead and nickel) were compared under

101 rk, the concentrations of Arsenic, Antimony, Cadmium, Chromium, Lead, Selenium and Vanadium were eval

102 lationship of urine metals including barium, cadmium, cobalt, cesium, molybdenum, lead, antimony, tha

103 toxic metals and trace elements (aluminium, cadmium, cobalt, copper, chromium, mercury, manganese, m

104 e ligand (1,10-phenanthroline) for precursor cadmium complex that works as a chelating agent in order

105 activity of the free quercetin and quercetin-cadmium complexes were determined by DPPH and ABTS assay

106 %) for the highest versus lowest category of cadmium concentration and 1.66 (95% confidence interval:

107 he Ala/Ala genotype had higher intracellular cadmium concentration and lower cell viability than thei

108 h 1,416 cases and 5,083 controls) on urinary cadmium concentration in relation to breast cancer risk.

109 l studies of the association between urinary cadmium concentration, a biomarker of cadmium exposure,

110 , evaluated by creatinine-normalized urinary cadmium concentration, and invasive breast cancer among

111 ntinuous variable (per 2-fold higher urinary cadmium concentration, hazard ratio = 0.94, 95% confiden

112 for each 0.5-microg/g creatinine increase of cadmium concentration.

113 Cadmium concentrations decreased rapidly during depurati

114 It was found that cadmium concentrations in all Thai herb samples were les

115 tiplex cadmium biosensors were responsive to cadmium concentrations ranging from 0.01 to 10microgml(-

116 rapace length and mercury, methylmercury and cadmium concentrations, and between fat and arsenic and

117 studies focusing on the cellular toxicity of cadmium-containing semiconductor quantum dots.

118 A positive correlation between islet cadmium content and both age (p = 0.048, R(2) = 0.09) an

119 re can be continuously tailored by modifying cadmium content or temperature.

120 Relatively high arsenic and cadmium contents were found within Australian prawns, bu

121 -MS for their content of aluminium, arsenic, cadmium, copper, lead and mercury in the dry product and

122 termination of trace level concentrations of cadmium, copper, lead, and silver as model analytes has

123 nd determination of trace amounts of silver, cadmium, copper, mercury, and lead from some food sample

124 01, and 0.08 ng/mL were obtained for silver, cadmium, copper, mercury, and lead with enrichment facto

125 method of separation and preconcentration of cadmium, copper, nickel, lead and zinc at trace level us

126 Some cadmium data is also presented, available with ICP-MS an

127 directed at increasing iron while decreasing cadmium density in the edible portions of crops and impr

128 CadC is a sequence-specific, DNA-binding and cadmium-dependent regulator of CadA, an efflux pump conf

129 s, as a novel alternative method for in situ cadmium detection, may reduce human exposure by compleme

130 n reflux system employing cold finger, being cadmium determined by ETAAS.

131 Cadmium doped antimony oxide (Cd-doped Sb2O4) nanostruct

132 we report surface reconstruction induced by cadmium doping into the [Au23(SR)16](-) (R = cyclohexyl)

133 For example, although cadmium elicited an adverse effect at the organismal lev

134 As such, cadmium environmental contamination poses a significant

135 ins could be successfully discriminated from cadmium exposed ones with a high heterogeneity value.

136 -2/Bcl-xL were dramatically increased in the cadmium-exposed transformed cells.

137 Environmental cadmium exposure has been associated with risk of breast

138 paring the highest to the lowest category of cadmium exposure in the general population, the weighted

139 This suggests that the duration of cadmium exposure influences the depuration rate for this

140 Our results show that cadmium exposure is associated with DNA hypermethylation

141 ot support the hypothesis that environmental cadmium exposure is associated with risk of postmenopaus

142 This meta-analysis suggests that a high cadmium exposure may be a risk factor for breast cancer,

143 vidence does not support the hypothesis that cadmium exposure may increase the risk of prostate cance

144 We aimed to evaluate the association of cadmium exposure with the risk of prostate cancer in bot

145 rinary cadmium concentration, a biomarker of cadmium exposure, and breast cancer risk.

146 spectively assessed the relationship between cadmium exposure, evaluated by creatinine-normalized uri

147 rmed for studies of prostate cancer risk and cadmium exposure.

148 ity than their Ala/Thr counterpart following cadmium exposure.

149 ostasis while supporting PC synthesis during cadmium exposure.

150 no genes were differentially expressed after cadmium exposure.

151 ctivity) toxicity in acute (96 h) copper and cadmium exposures, using the shallow-water ecophysiologi

152 , the highest quartile (vs. lowest) of blood cadmium had an odds ratio of 3.03 (95% CI: 1.44, 6.40) f

153 Cadmium had negative effects on macrophytes at much lowe

154 Following incubation with cadmium, higher intracellular cadmium was detected in cu

155 st cadmium toxicity was investigated using a cadmium-hypersensitive strain of Saccharomyces cerevisia

156 thaliana and has a key function in zinc and cadmium hypertolerance and hyperaccumulation in the extr

157 imental results show that simultaneous trace cadmium(II) and copper(II) ions can be quantitatively pr

158 s a new solid-phase method for extraction of cadmium(II) and copper(II) ions.

159 method is presented for the determination of cadmium(II) and lead(II) in various food and water sampl

160 The flexible coordination spheres of its cadmium(II) centers allow the receptor to dynamically ad

161 Substituting the cadmium(II) ions for copper(I) by switching solvent prom

162 ed from either zinc(II) tetrafluoroborate or cadmium(II) trifluoromethanesulfonate.

163 The removal efficiency of heavy metal ions (cadmium(II), Cd(II); cobalt(II), Co(II); nickel(II), Ni(

164 mium in adults and exposure to environmental cadmium in adolescents may play a role in the risk of he

165 gest that exposure to environmental lead and cadmium in adults and exposure to environmental cadmium

166 The mean values for lead and cadmium in domestic cultivated and imported rice were co

167 Subsequent accumulation of cadmium in food and drinking water can result in acciden

168 applied for trace determination of lead and cadmium in fruit (Citrus limetta, Kiwi and pomegranate)

169 A method for the determination of cadmium in herb samples based on solidified floating org

170 Widespread presence of cadmium in soil and water systems is a consequence of in

171 ion of zinc, manganese, nickel, calcium, and cadmium in sorghum seeds.

172 14, established the concentration limits for cadmium in specific products based on cocoa and chocolat

173 creased during chronic long term exposure to cadmium in the BEAS-2B cells as well as antiapoptotic pr

174 temperatures (for example, 80 degrees C for cadmium in Ti2PTe2).

175 e SCMFC could rapidly detect the presence of cadmium in water with high sensitivity (0.2 mug l(-1) cm

176 Cadmium-incorporated Li2FeSiO4/C composites have been su

177 mparing quintiles of energy-adjusted dietary cadmium intake.

178 ry-based sensor usually adopted for lead and cadmium ion detection.

179 rm and (ii) titanium phosphate nanoparticles-cadmium ion-mouse anti-PA antibodies (TiP-Cd(2+)-MalphaP

180 ere achieved by electrochemical detection of cadmium ions and lead ions with square wave voltammetry

181 Further, the cadmium ions bind strongly to the sensing surface than o

182 ic determination of trace levels of lead and cadmium ions in fruit and water samples.

183 conditions, the detection limit for lead and cadmium ions was 1.2 mug L(-1) and 0.2 mug L(-1), respec

184 We found little evidence that dietary cadmium is a risk factor for breast, endometrial, or ova

185 Cadmium is a toxic and persistent heavy metal with estro

186 Cadmium is a well known mutagenic metal that can enter c

187 Cadmium is a widespread heavy metal pollutant that may a

188 biologically active metals, such as lead and cadmium, is an important risk factor for cardiovascular

189 rapid method for the direct determination of cadmium, lead and copper in milk and fermented milk prod

190 copper and zinc) and heavy metals (chromium, cadmium, lead and nickel) were determined in varieties o

191 unexplored soluble chalcogenidometallates of cadmium, lead, and bismuth.

192 tary intake and biomarker levels of arsenic, cadmium, lead, and mercury among Asian populations in th

193 d consumption and dietary intake of arsenic, cadmium, lead, and mercury by combining 24-hr dietary in

194 rvey the levels of some heavy metals such as cadmium, lead, chromium, nickel and cobalt in domestic c

195 have considerably higher biomarker levels of cadmium, lead, mercury, and arsenic than whites, blacks,

196 have considerably higher biomarker levels of cadmium, lead, mercury, and arsenic than whites, blacks,

197 n of participants above and below the median cadmium level.

198 The combinations of three cadmium levels (0 [control] and 0.25 and 1 milligrams pe

199 yl substances and elements, such as arsenic, cadmium, mercury and lead.

200 blood lead and cadmium (n = 6,796) and urine cadmium (n = 2,093) levels with LTL among a nationally r

201 We examined associations of blood lead and cadmium (n = 6,796) and urine cadmium (n = 2,093) levels

202 EWI for cadmium, nickel, chromium through imported and domestic

203 l with the increased intracellular levels of cadmium observed in the mutant yap1.

204 2, and CDCl3, oleate ligands, in the form of cadmium oleate and Cd(x)OA(y) clusters, desorb.

205 t alkylamines slow down the reaction between cadmium oleate and trialkyl phosphine selenide by bindin

206 ive association was identified between blood cadmium or lead levels or urine arsenic level and a diag

207 drophila or Vibrio harveyi) or heavy metals (cadmium or lead) significantly increased the expression

208 ybdenum-doped indium oxide, dysprosium-doped cadmium oxide, graphene and diffused semiconductors, but

209 reast cancer was not associated with urinary cadmium parameterized either in quartiles (comparing hig

210 able signal reporters (apoferritin templated cadmium phosphates (ATCP) and apoferritin templated lead

211 Indium and cadmium play different but complementary roles in modify

212 t of Arabidopsis leaves with the heavy metal cadmium produces time course-dependent changes in peroxi

213 barium (Ptrend = 0.13), 0.74 (0.51-1.09) for cadmium (Ptrend = 0.35), 1.21 (0.85-1.72) for cobalt (Pt

214 steady-state concentration of intracellular cadmium, regardless of the cell's nutritional state.

215 The synthesized nanohybrid has high cadmium removal capacity and holds promising prospects f

216 The protein used was rubredoxin in which cadmium replaced the iron at the iron-sulphur site.

217 regulator of CadA, an efflux pump conferring cadmium resistance.

218 istinguishing molecular features of lead and cadmium resistant bacteria using Attenuated Total Reflec

219 et zinc levels and support prior evidence of cadmium's higher bioavailability in women and its long t

220 trodes that serves to passivate and dope the cadmium selenide nanocrystal channel layer.

221 Metallic silver and semiconducting cadmium selenide nanocrystals are deposited to form high

222 isplace the carboxylate surface ligands from cadmium selenide nanocrystals, oleic acid impurities are

223 We demonstrated this concept in cadmium selenide nanorods with gold tips, in which the g

224 s substitutional dopants in superlattices of cadmium selenide or lead selenide nanocrystals when the

225 rch has been conducted on materials based on cadmium selenide primarily due to its many years of deve

226 ion of the tri-n-octylphosphine oxide capped cadmium selenide quantum dots (QD) Langmuir monolayer.

227 rational structure of the atomically precise cadmium selenide quantum dots Cd35Se20X30L30, Cd56Se35X4

228 from molecular vibrations to bulk phonons in cadmium selenide quantum dots for the first time.

229 ed by transient absorption spectroscopy that cadmium selenide semiconductor nanoparticles, selectivel

230 hich the gold plasmon was strongly damped by cadmium selenide through interfacial electron transfer.

231 nd I-III-VI2 semiconductor materials such as cadmium selenide, which exist as two stable phases, cubi

232 de monolayers (2D-WS2) and a single layer of cadmium selenide/zinc sulfide core/shell 0D-QDs.

233 ed using solvothermal conversion of the same cadmium selenophenolate precursor (Me4N)2[Cd(SePh)4]: th

234 Cadmium showed a rather inconsistent influence on Fe def

235 b transcript expressions were observed under cadmium stress.

236 agram of cation-exchange (CE) chemistry from cadmium sulfide (CdS) into Cu(2-x)S nanowires (NWs) is r

237 We show that cadmium sulfide (CdS) nanocrystals can be used to photos

238 Cadmium sulfide (CdS) quantum dots (<10 nm in size) have

239 The model system, Moorella thermoacetica-cadmium sulfide (CdS), combines an inorganic semiconduct

240 ng polarization charges created at the metal-cadmium sulfide interface under strain to gate/modulate

241 420 nm, 1 sun), suspensions of ligand-capped cadmium sulfide nanocrystals in formic acid/sodium forma

242 Biologically precipitated cadmium sulfide nanoparticles served as the light harves

243 etic bacterium, Moorella thermoacetica, with cadmium sulfide nanoparticles, enabling the photosynthes

244 This paper describes the use of cadmium sulfide quantum dots (CdS QDs) as visible-light

245 Here, using a well-defined model system of cadmium sulfide-gold nanorods, we address the effect of

246 e graphene sheets were chemically doped with cadmium sulphide (CdS).

247 CSH, modulating the growth of CSH-stabilized cadmium sulphide quantum dots (CdS QDs).

248 cal polishing (CMP) is developed for mercury cadmium telluride (HgCdTe or MCT) semiconductors.

249 ng pass filter in combination with a mercury cadmium telluride detector was used to reduce the instru

250 To demonstrate such assemblies, we combine cadmium telluride nanoparticles with cytochrome C protei

251 We synthesized cadmium telluride quantum dots (CdTe QDs) capped with th

252 predator organism to determine the impact of cadmium telluride quantum dots (CdTe QDs).

253 nance energy transfer with l-cysteine-capped cadmium telluride quantum dots (CdTe-QDs) in aqueous sol

254 with the lowest manufacturing GHG footprint (cadmium telluride) are deployed in locations with the mo

255 ted by amorphous silicon, crystalline n-type cadmium telluride, and hydrogenated amorphous silicon.

256 provides facile composition control akin to cadmium telluride.

257 Thioglycolic acid (TGA)-capped cadmium-telluride (CdTe) quantum dots (QDs) exposing gre

258 ing a fast thermoelectrically cooled mercury-cadmium-telluride detector.

259 to compete with the state-of-the-art mercury-cadmium-telluride material system in the field of infrar

260 ing a series of pyramidal nanostuctures with cadmium terminated {111} facets.

261 ivalent metal cations, including heavy metal cadmium, the accumulation of which has been associated w

262 While the food samples almost do not contain cadmium, they have included lead at low levels of 0.13-1

263 urprisingly, the AtPCS1 mutants that enhance cadmium tolerance and accumulation are catalytically les

264 AtPCS1) yields mutants that confer levels of cadmium tolerance and accumulation greater than expressi

265 insight into biological pathways underlying cadmium toxicity and chronic disease risks.

266 ch program on trace elements with a focus on cadmium toxicity but soon thereafter began my research o

267 In addition, the cadmium toxicity exhibited by this strain is completely

268 reveal a novel protection mechanism against cadmium toxicity mediated by Yap1 that relies on the aer

269 reduced toxicity in both metals, but reduced cadmium toxicity significantly more.

270 tective action of blueberry extracts against cadmium toxicity was investigated using a cadmium-hypers

271 two derivatives 5a and 5e succeeded to treat cadmium toxicity.

272 ncreased copper toxicity, but did not affect cadmium toxicity.

273 Taken together, this study demonstrates that cadmium-transformed cells have acquired autophagy defici

274 The cadmium-transformed human lung bronchial epithelial BEAS

275 act of this variant on protein conformation, cadmium transport, activation of signalling pathways and

276 (GOF) mutants of a long MRP in yeast (Ycf1p cadmium transporter), a short yeast MRP (Yor1p oligomyci

277 and examine the relationship between urinary cadmium(UCd) and hypertension and impaired kidney functi

278 exposure and demonstrated a greater rate of cadmium uptake relative to the hepatopancreas.

279 The majority of cadmium uptake was localized within the gills and hepato

280 ion of FET4 and results in the impairment of cadmium uptake.

281 for 6 replicate measurements of 1.0mugL(-1) cadmium was +/-2.67%.

282 ncubation with cadmium, higher intracellular cadmium was detected in cultured human embryonic kidney

283 e synergistic interaction between copper and cadmium was not affected by low temperature, but high hy

284 (versus lowest) quartiles of blood and urine cadmium were associated with -5.54% (95% CI: -8.70, -2.3

285 est (vs. lowest) quartiles of blood lead and cadmium were associated with 1.70 (95% CI: 1.25, 2.31) a

286 ightly more effective at removing nickel and cadmium, while at pH 8.5, iron electrodes were more effe

287 Critical twinning stress of cadmium zinc telluride (CdZnTe or CZT) calculated is 1.3

288 mechanical polishing (CMP) is developed for cadmium zinc telluride (CdZnTe or CZT) wafers.

289 a 3-dimensional (3D) dynamic approach with a cadmium zinc telluride (CZT) camera.

290 regional MPR in multivessel patients using a cadmium zinc telluride camera appear to correlate well w

291 lity of perfusion reserve estimation using a cadmium zinc telluride camera in a cohort of multivessel

292 ator stress were performed using a dedicated cadmium zinc telluride camera.

293 r bolus injection of (123)I-mIBG on a hybrid cadmium zinc telluride SPECT/CT system.

294 The levels of cadmium, zinc and iron were measured in different vegeta

295 was developed for the determination of lead, cadmium, zinc, manganese and iron in white and wild rice

296 I-MIBG) uptake obtained using a multipinhole cadmium-zinc-telluride (CZT) camera with that obtained u

297 gamma-cameras with solid-state cadmium-zinc-telluride (CZT) detectors have better count

298 This study compared two SPECT cameras with cadmium-zinc-telluride (CZT) detectors to a conventional

299 ecent advances in SPECT technology including cadmium-zinc-telluride (CZT) semiconductor detector mate

300 myocardial perfusion imaging (MPI) with the cadmium-zinc-telluride (CZT) SPECT camera is not well es