ライフサイエンスコーパス: Pb

1 Pb isotope ratios showed notable alignments in binary mi

2 Pb-free germanium telluride (GeTe)-based material has re

3 vskites with the formula (A')(2) (A)(n) (-1) Pb(n) I(3) (n) (+1) have remarkable stability and promis

4 0.032 ug L(-1) (Cd(II)) and 0.015 ug L(-1) (Pb(II)) for A-MWCNT/Hyalu/l-Cys/GCE and 0.057 ug L(-1) (

5 0.057 ug L(-1) (Cd(II)) and 0.034 ug L(-1) (Pb(II)) for A-MWCNT/Hyalu/l-Ser/GCE.

6 synthesized layered Ruddlesden-Popper FA(n+1)Pb(n)X(3n+1) (FA = formamidinium, X = I, Br; n = number

7 h shuttles FAX salt pairs between the FA(n+1)Pb(n)X(3n+1) domains and adjacent FAX "reservoir" domain

8 only offer a single-color transition, FA(n+1)Pb(n)X(3n+1) films reversibly switch between multiple co

9 .034 (As), 0.015 (Cd), 0.021 (Hg) and 0.105 (Pb) mug g(-1), which are suitable to attain the maximum

10 /lead clusters, [Au(8)Pb(33)](6-) and [Au(12)Pb(44)](8-), both of which contain nido [Au@Pb(11)](3-)

11 chemically similar to phosphohedyphane (Ca(2)Pb(3)(PO(4))(3)(Cl,F,OH)((s))) when phosphate was presen

12 lloying Sn with Pb, in the series of (MBA)(2)Pb(1-x)Sn(x)I(4).

13 d iodide perovskites (BA)(2)(EA(x)MA(1-x))(2)Pb(3)I(10) (x = 0-1, BA is n-butylammonium, MA is methyl

14 2+), Al(3+), Ni(2+), Cu(2+), Zn(2+), Co(2+), Pb(2+) and Ru(3+)) and aqueous compatibility was demonst

15 erations simultaneously in Co(60)Fe(20)B(20)/Pb(Mg(1/3)Nb(2/3))(0.7)Ti(0.3)O(3) heterostructures base

16 (203)Pb-L1-(203)Pb-L5 were synthesized in high radiochemical

17 Conclusion: (203)Pb-L1-(203)Pb-L5 demonstrated favorable pharmacokinetics

18 f (212)Pb-L2 supports the corresponding (203)Pb/(212)Pb theranostic pair for PSMA-based alpha-particl

19 (203)Pb-L5 (31.0, 15.2) and lowest for (203)Pb-L2 (8.0, 4.2).

20 the tumor and kidneys were highest for (203)Pb-L5 (31.0, 15.2) and lowest for (203)Pb-L2 (8.0, 4.2).

21 Conclusion: (203)Pb-L1-(203)Pb-L5 demonstrated favorable pharmacokinetics for (212)P

22 Whole-body clearance of (203)Pb-L1-(203)Pb-L5 was fast.

23 tion and SPECT/CT imaging of (203)Pb-L1-(203)Pb-L5 were performed on mice bearing PSMA(+) PC3 PIP and

24 (203)Pb-L1-(203)Pb-L5 were synthesized in high radiochemical yield and s

25 Whole-body clearance of (203)Pb-L1-(203)Pb-L5 was fast.

26 biodistribution and SPECT/CT imaging of (203)Pb-L1-(203)Pb-L5 were performed on mice bearing PSMA(+)

27 the matching gamma-emitting surrogate, (203)Pb.

28 th high (143)Nd/(144)Nd and low (206)Pb/(204)Pb-lacking strong signatures of recycled materials.

29 lignments and to the measurement of the (204)Pb isotope, a precise characterization of the Pb isotope

30 mains-with high (143)Nd/(144)Nd and low (206)Pb/(204)Pb-lacking strong signatures of recycled materia

31 ncorrelated distributions of radiogenic (206)Pb and U are observed in several of the wetland soil sam

32 he structural environments of (13)C and (207)Pb change near T(C).

33 hifts were obtained by (1)H, (13)C, and (207)Pb magic angle spinning NMR and (14)N static NMR.

34 ime T(1rho) values for (1)H, (13)C, and (207)Pb nuclei increased with increasing temperature and did

35 erature, whereas those of the (13)C and (207)Pb nuclei varied near the phase transition temperature (

36 (79/81)Br, (87)Rb, (127)I, (133)Cs, and (207)Pb nuclei) and locally and shedding light onto the conne

37 s considering all possible (1)H-(133)Cs/(207)Pb spin pairs were then calculated.

38 erized by NMR ((1)H, (13)C, (119)Sn, or (207)Pb), electronic, and IR spectroscopy and by X-ray crysta

39 is a change in the surroundings of the (207)Pb nuclei in the PbBr(6) octahedra and of the C-N groups

40 carbon and nitrogen content), (14) C, (210) Pb and (137) Cs analyses and were used to infer changes

41 (210)Pb concentrations >= 1.0 pCi/L occurred most frequently

42 (210)Pb is mobilized by alpha recoil associated with the deca

43 sis of lifetime cancer risks, lead-210 ((210)Pb) and polonium-210 ((210)Po) >= 1.0 and 0.7 pCi/L (pic

44 e- (Fe-Mn-) oxyhydroxides (which adsorb (210)Pb) and formation of lead-carbonate complexes (enhancing

45 222)Rn) concentrations > 4000 pCi/L had (210)Pb >= 1.0 pCi/L.

46 tly where acidic groundwaters inhibited (210)Pb readsorption (felsic-crystalline rocks) and where red

47 (212)Pb-L2 also demonstrated an increased survival benefit in

48 bed radiation dose of the corresponding (212)Pb-labeled analogs was determined using the biodistribut

49 argeted low-molecular-weight agents for (212)Pb-based TRT of patients with prostate cancer (PC) by ev

50 nstrated favorable pharmacokinetics for (212)Pb-based TRT.

51 edian survival of 55 d for 277.5 kBq of (212)Pb-daratumumab instead of 11 d for phosphate-buffered sa

52 ftment with an intravenous injection of (212)Pb-daratumumab or control solution.

53 To evaluate the in vivo efficacy of (212)Pb-daratumumab, mice were engrafted subcutaneously with

54 re treated with 185 kBq or 277.5 kBq of (212)Pb-daratumumab.

55 creasing activity (0.185-3.7 kBq/mL) of (212)Pb-isotypic control or (212)Pb-daratumumab was evaluated

56 y study with a single administration of (212)Pb-L2 demonstrated dose-dependent inhibition of tumor gr

57 The antitumor efficacy of (212)Pb-L2 supports the corresponding (203)Pb/(212)Pb therano

58 kBq/mL) of (212)Pb-isotypic control or (212)Pb-daratumumab was evaluated.

59 b-L2 supports the corresponding (203)Pb/(212)Pb theranostic pair for PSMA-based alpha-particle TRT in

60 heless, acute toxicity experiments with (212)Pb-anti-mCD38 established a toxic activity of 277.5 kBq.

61 No toxicity was observed with (212)Pb-daratumumab up to 370 kBq because of lack of cross-re

62 s observed after 3 d of incubation with (212)Pb-daratumumab, compared with (212)Pb-isotypic control o

63 with (212)Pb-daratumumab, compared with (212)Pb-isotypic control or cold antibodies.

64 (CH(3) (CH(2) )(3) NH(3) )(2) (CH(3) NH(3) )Pb(2) Br(7) (n = 2) layers undergo two distinct phase tr

65 , model oil paints with lead white (2PbCO(3).Pb(OH)(2)) and zinc white (ZnO) pigments, which are freq

66 pigment lead white (hydrocerussite, 2PbCO(3).Pb(OH)(2)).

67 e synthesis of two gold/lead clusters, [Au(8)Pb(33)](6-) and [Au(12)Pb(44)](8-), both of which contai

68 cipitation with Mg(OH)(2) and using either a Pb double spike or external normalization to Tl for mass

69 Utilizing a Pb(2)Ru(2)O(7-delta) pyrochlore O(2)-evolution electroca

70 ss accurate, especially when combined with a Pb double spike for mass bias correction.

71 s and structures of single-crystal (BA)(2)(A)Pb(2)I(7) where BA = butylammonium and A = methylammoniu

72 bson family, with the general formula (A')(A)Pb(2)Br(7) ((A' = 3-(aminomethyl)piperidinium (3AMP) and

73 oconversion between the blue light-absorbing Pb and green light-absorbing Pg states, as well as therm

74 The most accurate Pb isotope data are produced following Nobias extraction

75 stead, the Ag-centered nido icosahedron, [Ag@Pb(11)](3-), is the only isolated product.

76 orption spectroscopy showed that >90% of all Pb species in remediated soils were converted to PLJ, an

77 ot yet been reported (for Pb(4)S(3)Br(2) and Pb(3)S(2)Cl(2)) can be prepared on the nanoscale by wet-

78 region marine species had the lowest As and Pb contents.

79 scale precipitates, discordant Ag atoms, and Pb/Sr, Pb/Ba point defects in the PbSe matrix work toget

80 e extractions of Mn, Co, Ni, Cu, Zn, Cd, and Pb ions from natural water samples prior to ICP-MS deter

81 ereas the reduction in levels of Hg, Cd, and Pb was much lower.

82 l elements, including Mo, Er, Na, Li, Cs and Pb, varied by 10-fold across the 14 wines.

83 Removal of dissolved Cd, Cu, and Pb in BCZ sediments caused steep vertical gradients at t

84 s change towards less radiogenic Nd, Hf, and Pb isotope ratios.

85 100 and 92% were obtained for As, Cd, Hg and Pb, respectively, when 7 mol L(-1) HNO(3) was used as th

86 he first time for subsequent As, Cd, Hg, and Pb determination by atomic absorption spectroscopy techn

87 ces in the quantification of As, Cd, Hg, and Pb.

88 ent was linearly dependent on the Cd(II) and Pb(II) concentrations in the range from 0.4 to 4 ug L(-1

89 eveloped for the determination of Cd(II) and Pb(II) in bivalve mollusks using square wave anodic stri

90 tinguish between Cu(II), Cd(II), Hg(II), and Pb(II) at a concentration of 100 muM.

91 endments slightly increased total Cd, Ni and Pb in soil, but Cd and Ni concentration was below allowa

92 tentially toxic elements (As, Cr, Hg, Ni and Pb) varied from 0.9 to 1.4, pointing to a similar distri

93 ees N, coincident with high dissolved Pb and Pb isotope ratios matching Asian industrial sources and

94 The indirect band gaps of the Sn and Pb compounds are ~1.7 and 2.0 eV, respectively, which is

95 for Pb in both remediated natural soils and Pb-mineral spiked soils were reduced by >90% relative to

96 d between the geogenic and the anthropogenic Pb isotopes data that characterize European and Asian so

97 We treated two soils with anthropogenic Pb contamination and samples of clean topsoil spiked wit

98 ates from dynamic octahedral rotation around Pb caused by anharmonic vibration of Cl atoms induced by

99 ed diffraction data from a single crystal as Pb or after irradiation with blue light, detected photoc

100 arable to several commercial devices such as Pb-acid and Ni/MH batteries.

101 ective indirect proxy for reliably assessing Pb emissions directly linked to human activities.

102 ericas, which show low levels of atmospheric Pb until the Industrial Revolution.

103 )Pb(44)](8-), both of which contain nido [Au@Pb(11)](3-) icosahedra surrounding a core of Au atoms.

104 ondary pai-type interactions between the [Au@Pb(11)](3-) ligands and the gold core play a significant

105 the new (3AMP)(a)(4AMP)(1-a)(FA)(b)(MA)(1-b)Pb(2)Br(7) perovskites.

106 ce elements (Li, Mg, Mn, Ni, Co, Cu, Sr, Ba, Pb) via chemometric evaluation facilitated classificatio

107 The most abundant element is found to be Pb (med = 4.6 x 10(6) ng m(-3)), which is 40 times the s

108 ral distortion, the nearest distance between Pb and Fe is found to be 3.39(1) angstrom.

109 e differences of tolerant mechanisms between Pb(2+) and Cd(2+) in Enterobacter sp.

110 esults and revealed that highly bioavailable Pb (hydroxy)carbonate (indicative of Pb-based paint) was

111 During childhood, ingestion of bioavailable Pb in contaminated soils can be a major route of Pb abso

112 Bone and blood Pb levels were significantly lower (P < 0.001, Student's

113 u, 9.6 mug/g; hair Cr, 0.05 mug/g; and blood Pb, 1.3 mug/dL.

114 2014 may be attributable to decreased blood Pb levels.

115 % CI 6.2 to 48%, P < 0.01) of elevated blood Pb, compared with children in houses served by a communi

116 It is based on a curated dataset of blood Pb records from 59,483 North Carolina children matched w

117 To understand potential impacts on blood Pb levels (BLLs) from drinking water Pb reduction action

118 stical associations between children's blood Pb and household drinking water source.

119 In full-length Syt1, both Pb(2+)-complexed C2 domains associate with phosphatidyls

120 ptical properties where the larger the Pb-Br-Pb angle, the narrower the band gap.

121 rary, higher FA fractions increase the Pb-Br-Pb angles.

122 tural analogue of the recently reported bulk Pb(3)Se(2)Br(2) phase.

123 r outcomes previously found to be altered by Pb, PS, or combined Pb and PS in F1 offspring: behaviora

124 ygenase), contaminants heavy metals (As, Cd, Pb, and Hg), antinutrient phytic acid and hazardous coli

125 Na, P, Se and Zn) and trace metals (As, Cd, Pb, U and V).

126 L and b) and the glucose, sucrose, Brix, Cd, Pb, Ni, Zn, and Cr values were found in the highland hon

127 cently discovered high-pressure chalcohalide Pb(4)S(3)I(2) phase, and indeed we were able to extend o

128 (Co, Cd, 85 degrees C), long duplicates (Co, Pb, 85 degrees C), and insertions (Co, Mn, 85 degrees C)

129 y found to be altered by Pb, PS, or combined Pb and PS in F1 offspring: behavioral performance [fixed

130 Ca, Fe, Zn, Hg, Se, As, Cu, Cd, Mn, Ni, Cr, Pb and Co) were determined in dorsal white and dark musc

131 a novel sensor was utilized for determining Pb(II) ions in natural water and in fruit juice with ver

132 35 degrees N, coincident with high dissolved Pb and Pb isotope ratios matching Asian industrial sourc

133 understanding of determinants of house dust Pb bioavailability.

134 omes Survey (AHHS) was developed to estimate Pb exposure from house dust and soil, in addition to oth

135 ing representative metal ions were examined: Pb, Cd, Zn, Ce (III), Ba, Ni, Fe(II), Fe(III), Cu(II), C

136 idered across lineages, F3 females exhibited Pb-related alterations in behavior, striatal BDNF levels

137 Maternal F0 Pb exposure produced runting in F3 offspring.

138 as the experimental results where (3AMP)(FA)Pb(2)Br(7) has the smallest band gap while (4AMP)(MA)Pb(

139 potentially toxic elements (Cu, Cr, Mn, Fe, Pb, Zn, Ni) were analysed by atomic absorption spectrome

140 was dominantly present in the water as fine Pb(II) orthophosphate particles.

141 f seawater Pb isotope compositions following Pb separation by either solid-phase extraction with Nobi

142 0.39, 0.060, 0.021, and 0.025 ng mL(-1) for Pb(II), Cu(II), Cd(II), and Zn(II) cations, respectively

143 -1) for Ni(II), 0.041 and 0.14 ng mL(-1) for Pb(II), respectively.

144 mug L(-1) for Cd(II) and 8.49 mug L(-1) for Pb(II).

145 U) filters and pitcher filters certified for Pb and particulate reduction under NSF/ANSI Standards 53

146 Estimated RBA for Pb in both remediated natural soils and Pb-mineral spike

147 ructures that had not yet been reported (for Pb(4)S(3)Br(2) and Pb(3)S(2)Cl(2)) can be prepared on th

148 rkable that one high-pressure structure (for Pb(4)S(3)I(2)) and two metastable structures that had no

149 Altering the metal from Pb(II) to Hg(II) or shifting the relative position of th

150 ruggled with elevated lead (Pb) release from Pb service lines and domestic plumbing in the zone fed b

151 recently developed 2D perovskite (HA)(2) (GA)Pb(2) I(7) (HA=n-hexylammonium, GA=guanidinium).

152 Separating this global Pb pollution signal into regionally representative clust

153 th anomalous (182)W and examine how Sr-Nd-Hf-Pb isotopic variations-useful for tracing subducted, rec

154 (Pb(3)O(4)) and lead white (hydrocerussite [Pb(3)(CO(3))(2)(OH)(2)] and/or cerussite [PbCO(3)]) were

155 become greatly distorted, with one of the I Pb I angles approaching 82 degrees compared to the ideal

156 nd increases the optical bandgap, while Pb-I-Pb tilting angles play a secondary role.

157 orbitals in the band gap transition of A(II) Pb(2) X(6) .

158 fords the expanded perovskite analogs: A(II) Pb(2) X(6) .

159 The devices were applied for Cd(II), Pb(II), Cu(II), Fe(II), and Ni(II) determination in PM s

160 .5, 1.0, 0.5, and 1.0 mug L(-1), for Cd(II), Pb(II), Cu(II), Fe(II), and Ni(II), respectively.

161 e Seebeck coefficient of ~ -230 muV K(-1) in Pb(0.98)Bi(0.02)Se is close to the golden range, leading

162 Our results demonstrate that decreases in Pb exposure can result in large benefits for the adult p

163 This work aims to (i) identify variations in Pb levels in North Carolina school and child care drinki

164 This increased Pb exposure is likely a result of corrosion of household

165 They are tetrahedral PbBr(4) (2-) ions (Pb-Br = 3.091(11) angstrom) surrounded by Na(+) and Cs(+

166 The odds that a greater than 5 mug/L Pb level is detected has been decreasing over the years,

167 chanism of white-light emission from layered Pb-X (X = Cl or Br) perovskites following UV excitation

168 nous detection of cadmium (Cd(II)) and lead (Pb(II)) was obtained by acid treated multiwalled carbon

169 to light the presence of iron (Fe) and lead (Pb) compounds in the majority of the red inks inscribed

170 l records of anthropogenic atmospheric lead (Pb) spanning the last 4000 years, an effective indirect

171 inations of cobalt (Co), cadmium (Cd), lead (Pb), and manganese (Mn).

172 mental and health risk as they contain lead (Pb(2+)) and are readily soluble in water.

173 ble semiconductors that do not contain lead (Pb) or cadmium (Cd).

174 ew Jersey, has struggled with elevated lead (Pb) release from Pb service lines and domestic plumbing

175 of lead-carbonate complexes (enhancing lead (Pb) mobility).

176 We measured manganese (Mn), lead (Pb), copper (Cu), and chromium (Cr) in hair, blood, urin

177 ry (Hg), nickel (Ni), molybdenum (Mo), lead (Pb), antimony (Sb), tin (Sn), and thallium (Tl) were mea

178 Forms of lead (Pb) have been insidiously invading human life for thousa

179 M transport determined from radiogenic lead (Pb) isotopes varied from 0 to 59% (mean 37%) Asian-sourc

180 ring in mind that pigments such as red lead (Pb(3)O(4)) and lead white (hydrocerussite [Pb(3)(CO(3))(

181 Exposure to lead (Pb) during early life has persistent adverse health effe

182 hese issues, we exposed Moina dubia to lead (Pb, 50 mug/L) under two temperatures (25 and 28 degrees

183 Compared with lead (Pb)- and mercury (Hg)-based liquid metal electrodes, the

184 bO(2) material and react with divalent lead [Pb(II)] at the surface of a basal litharge (PbO) layer.

185 Lone pair cations like Pb(2+) are extensively utilized to modify and tune physi

186 a previous report that plumbojarosite lowers Pb RBA in soils.

187 ack pepper had the highest Mn and the lowest Pb contents.

188 ide perovskite semiconductors, 2D (BA)(2)(MA)Pb(2)I(7) (with MA = CH(3)NH(3), and BA = CH(3)(CH(2))(3

189 , where the Rashba coefficient in (BA)(2)(MA)Pb(2)I(7) is estimated to be about 7 times larger than t

190 5% and 0.11% for the MAPbI(3) and (BA)(2)(MA)Pb(2)I(7), respectively.

191 0.22% and ~0.20% for MAPbI(3) and (BA)(2)(MA)Pb(2)I(7), respectively.

192 7) has the smallest band gap while (4AMP)(MA)Pb(2)Br(7) has the largest band gap.

193 rroelectric two-dimensional DJ-OIHP (AMP)(MA)Pb(2)I(7) (DJP(n=2), AMP = 4-(aminomethyl)piperidinium;

194 (indicative of Pb-based paint) was the major Pb species present in house dusts.

195 (23%) in a residential soil where the major Pb species was found to be plumbojarosite, consistent wi

196 Maternal Pb and PS exposures were carried out in F0 mice.

197 a thiophilic, trigonal pyramidal metalloid (Pb(II)) that binds to these sulfurs and (3) an adjacent

198 organic spacer for the fabrication of mixed Pb/Sn-based perovskites, exhibiting a narrow bandgap of

199 ons (90th percentiles) of the mixture of Mn, Pb, and Cr (0.3 mug/g, 2.6 mug/dL, and 0.1 mug/g, respec

200 Higher adolescent levels of Mn, Pb, and Cr were associated with lower IQ scores, especia

201 phosphate [P], or sulfate) to convert native Pb species to PLJ and used a mouse assay to assess relat

202 culated as 0.7 uA/nM (Cd(II)) and 3.5 uA/nM (Pb(II)) for A-MWCNT/Hyalu/l-Cys/GCE and 0.6 uA/nM (Cd(II

203 ys/GCE and 0.6 uA/nM (Cd(II)) and 2.6 uA/nM (Pb(II)) for A-MWCNT/Hyalu/l-Ser/GCE.

204 This research confirmed that nonadherent Pb(II)-orthophosphate nanoparticles were an important fo

205 The application of a novel Pb(2+) selective sensor based on the ionic imprinted pol

206 ths ranging from 2.21 to 2.31 angstrom and O-Pb-O bond angles ranging from 72 degrees to 75 degrees .

207 ation of the high stereochemical activity of Pb(2+) with the extremely strained [Zn(2)Ga(2)O(7)](4-)

208 e levels, and (iii) evaluate the adequacy of Pb reporting limits according to modern instrumentation.

209 ration and determination of trace amounts of Pb(II), Cu(II), Cd(II), and Zn(II) ions, using a mini-co

210 y challenges associated with the analysis of Pb isotopes in seawater.

211 The application of Pb isotopes to marine geochemistry is currently hindered

212 peculiar distribution and colocalization of Pb, phosphorus (P), and sulfur (S), which are present at

213 00 nm) and their aggregates were composed of Pb, phosphorus, and chlorine, which are consistent with

214 al behavioral or biochemical consequences of Pb exposure, and modification of any such effects by PS,

215 Sr and Ba atoms diminish the contribution of Pb 6s(2) states and decrease the energy of the light hol

216 The individual and interactive effects of Pb, temperature, and predator cues on M. dubia were stro

217 ferroelectric domains in ultrathin films of Pb(Zr(0.4)Ti(0.6))O(3) results in a maze, or labyrinthin

218 hate nanoparticles were an important form of Pb in drinking water in the Pequannock water quality zon

219 e most useful in understanding the impact of Pb exposure on CVD mortality risk in adults.

220 Here we report that the incorporation of Pb(2+) into the polar "114"-type structure of CaBaZn(2)G

221 ailable Pb (hydroxy)carbonate (indicative of Pb-based paint) was the major Pb species present in hous

222 Levels of Pb in some samples exceed the maximum allowable level, b

223 chanism, together with the lower mobility of Pb cations, caused higher microbial tolerance and remova

224 nally, we could also prepare nanocrystals of Pb(3)S(2)Cl(2), which proved to be a structural analogue

225 lly affect the overall adsorption process of Pb(II) on H(2)SO(4)-treated CNS.

226 in contaminated soils can reduce the RBA of Pb and minimize this medium's role as a source of Pb exp

227 to assess relative bioavailability (RBA) of Pb in untreated (U) and remediated soils.

228 n contaminated soils can be a major route of Pb absorption.

229 cells work as 'hot spots' on the sorption of Pb NPs.

230 d minimize this medium's role as a source of Pb exposure for young children.

231 The peaks in the emission spectra of Pb,Br,H,Cs,Na-X and the CsPbBr(3) NCs are both at about

232 In the study of Pb(II) removal, various models of adsorption kinetics an

233 Results showed, the mean values of Pb and Zn were higher in crop than Food and Agriculture

234 Our work is mainly focused on Pb(4)S(3)Br(2), a chalcohalide phase unknown to date tha

235 contribute to guiding future legislation on Pb testing.

236 a (xAMPY)M(2)I(6) (x = 3 or 4, M = Sn(2+) or Pb(2+)) which is double of the AMX(3) formula.

237 centrations of toxic minerals like As, Cd or Pb.

238 s, while d sites provide pure Pb(II)C(2)D or Pb(II)CD(2) scaffolds.

239 (C(6)H(2)-2,4,6-Pr(i)(3))(2); M = Ge, Sn, or Pb) under mild conditions (<=80 degrees C, 1 bar) afford

240 e, Bi, Cd, Co, Cr, Cu, K, Mn, Mo, Na, Ni, P, Pb, Th, Tl, Sb, U, V, Y and Zn) in 73 commercial product

241 us study that demonstrated high RBA of paint Pb added to soil.

242 . house dust contaminated in situ with paint Pb and corroborates results from a previous study that d

243 intensive studies on the complex perovskite Pb(Fe(2/3)W(1/3))O(3) (PFWO) relaxor, understanding the

244 ht the need for targeted outreach to prevent Pb exposure for the 42.5 million Americans depending on

245 The zeolite X product, Pb,Br,H,Cs,Na-X, shows superior stability toward moistur

246 )B heterotrimers, while d sites provide pure Pb(II)C(2)D or Pb(II)CD(2) scaffolds.

247 ine, which are consistent with pyromorphite, Pb(5)(PO(4))(3)Cl.

248 the accurate determination of the radiogenic Pb percentages in the cores that were overall found to b

249 SL replacement coupled with CCT for reducing Pb in drinking water and children's BLLs, and (2) in som

250 for preconcentration of As, Cd, Cr, Co, Sb, Pb and Tl to inductively coupled plasma optical emission

251 rometry (MC-ICP-MS) measurements of seawater Pb isotope compositions following Pb separation by eithe

252 e-spike method and produce unbiased seawater Pb isotope compositions with similar or improved precisi

253 kites (X=halide) with a pair of edge-sharing Pb-X octahedra affords the expanded perovskite analogs:

254 rticosterone levels, whereas F3 males showed Pb- and PS-related alterations in behavior and total per

255 A similar Pb, P, and S composition was found in three black inks,

256 alogues XM(YCH(2)CH(2))(3)N (M = Si, Ge, Sn, Pb, Ti, Al, Cr, Fe, Ni...; Y = O, NR, CH(2), S), i.e., s

257 Our laboratory-based approach for soil Pb remediation uses addition of iron (Fe) sulfate and ap

258 of plumbojarosite (PLJ), a sparingly soluble Pb-Fe hydroxysulfate mineral.

259 aried from 0 to 59% (mean 37%) Asian-sourced Pb at high elevation, whereas stronger regional PM input

260 cro-Fourier transform infrared spectroscopy, Pb is shown to be associated with fatty acid phosphate,

261 recipitates, discordant Ag atoms, and Pb/Sr, Pb/Ba point defects in the PbSe matrix work together to

262 Stable Pb isotope ratios were measured and compared to U distri

263 on of EA in the cage significantly stretches Pb-I bonds, expands the cage, and induces a larger octah

264 Strikingly, Pb-induced reduction in the performance of M. dubia was

265 d by the fractionation filters revealed that Pb was dominantly present in the water as fine Pb(II) or

266 The Pb(4)S(3)Br(2) nanocrystals herein feature a remarkably

267 The Pb(II)-binding mechanism on an annealed hematite (1102)

268 ons between the 4a and 4b sites, and (3) the Pb displacement disorder is present in this material and

269 at on the length scale of the unit cell, the Pb I octahedra concurrently become greatly distorted, wi

270 e contrary, higher FA fractions increase the Pb-Br-Pb angles.

271 e CTR results, DFT calculations indicate the Pb binding energy at the ES(2) site is at least 0.16 eV

272 the optical properties where the larger the Pb-Br-Pb angle, the narrower the band gap.

273 b isotope, a precise characterization of the Pb isotope composition of the U-ore was performed withou

274 length elongation reduces the overlap of the Pb s- and I p-orbitals and increases the optical bandgap

275 -organic framework could capture most of the Pb(2+) leaked from the degraded perovskite solar cells b

276 Replacing the Pb-X octahedral building unit of A(I) PbX(3) perovskites

277 l studies and DFT calculations show that the Pb-I bond length elongation reduces the overlap of the P

278 ormation, calcium is frequently bound to the Pb(II) phosphate crystal lattice structure, causing meas

279 ith the local distortion environment of the [Pb(2)Br(7)] framework.

280 F3 females showing multiple changes through Pb-exposed lineages.

281 , as well as thermal reversion of Pg back to Pb.

282 ty that exposures of previous generations to Pb or PS may influence the brain and behavior of future

283 piked soils were reduced by >90% relative to Pb RBA for U soils, which is substantially more effectiv

284 were able to extend our synthesis scheme to Pb(4)S(3)I(2) colloidal nanocrystals, whose structure ma

285 ial tolerance and removal efficiency towards Pb(2+) .

286 Here, we present the first U-Pb CA-ID-TIMS zircon age (252.24 +/- 0.11 (2sigma) Ma) f

287 Here we present U-Pb ages for impact-driven shock-recrystallised accessory

288 raction, coprecipitation represents a useful Pb separation technique for samples with low to moderate

289 samples of clean topsoil spiked with various Pb compounds (i.e., carbonate, chloride, phosphate [P],

290 owledge, this is the first report of in vivo Pb RBA for U.S. house dust contaminated in situ with pai

291 n blood Pb levels (BLLs) from drinking water Pb reduction actions (i.e., combinations of lead service

292 data set spanning a range of realistic water Pb concentrations and variabilities showed BLL predictio

293 als and increases the optical bandgap, while Pb-I-Pb tilting angles play a secondary role.

294 centration was below allowable limits whilst Pb reached a hazardous level.

295 Alloying with Pb by element substitution increases the band gap of SnO

296 pyramid geometry is slightly distorted with Pb-O bond lengths ranging from 2.21 to 2.31 angstrom and

297 l activity are modulated by alloying Sn with Pb, in the series of (MBA)(2)Pb(1-x)Sn(x)I(4).

298 mine the electronic properties of the Sn(1-x)Pb(x)O ternary oxide system.

299 unexpected cell volume expansion of CaBa(1-x)Pb(x)Zn(2)Ga(2)O(7) (0 <= x <= 1), which is a unique str

300 sual evolution of the unit cell for CaBa(1-x)Pb(x)Zn(2)Ga(2)O(7) is due to the combination of the hig

301 Cysteine substitution in an a site yields Pb(II)A(2)B heterotrimers, while d sites provide pure Pb