activities ranging over 2 orders of magnitude, all yielding satisfactory results (Table 3). The IAEA-384, a Fangataufa Lagoon sediment, is a reference material designed for the determination of anthropogenic and natural radionuclides in sediment. 27 This material is certified for 10 radionuclides, including 210Pb ( 210Po in equilibrium), and information values are given for 10 radionuclides, including 226 226 -1 Ra. The Ra activity ranges from 2.0 to 2.9 Bq kg (95% confidence interval) with a median value of 2.4 Bq kg-1 , which is the low range of 226Ra activities in sediments. Dry sediment aliquots of 500 mg were analyzed by using the proposed method (N ) 15). Spectra were analyzed by using both a wide and a narrow counting window, and results are shown in Figure 9. The median of both distributions is 2.2 Bq kg-1 , and means were 2.3 Bq kg-1 (50 channels) and 2.5 Bq kg-1 (150 channels), very close to the reference material reported value and within its 95% confidence interval. The IAEA-385, a certified reference material for radionuclides in an Irish Sea sediment, is intended to be used, among other purposes, for the development and validation of radiometric and mass spectrometry analytical methods. 28 Its certified median value, 22.7 Bq kg-1 , is typical of most soils and sediments. The median value obtained with the proposed method (N ) 15) is 23.5 Bq kg-1 Figure 8. Calibration curve of unquenched , which, although slightly higher than the upper limit of the certified confidence interval, represents a deviation of only 7.3%. 226Ra. (27) Povinec, P. P.; Pham, M. K.; Sanchez-Cabeza, J. A.; Barci-Funel, G.; Bojanawski, R.; Boshkova, T.; Burnett, W.; Carvalho, F.; Chapeyron, B.; Cunha, I. L.; Dahlgaard, H.; Galabov, N.; Fifield, L.; Gaustaud, J.; Geering, J.-J.; Gomez, I. F.; Green, N.; Hamilton, T.; Ibanez, F. L.; Ibn Majah, M.; John, M.; Kanisch, G.; Kenna, T. C.; Kloster, M.; Korun, M.; Liong Wee Kwong, L.; La Rosa, J.; Lee, S.-H.; Levy-Plaomo, I.; Malatova, M.; Maruo, Y.; Michell, P.; Murciano, I. V.; Nelson, R.; Nouredine, A.; Oh, J.-S.; Oregioni, B.; Petit, G.; Pettersson, H. B. L.; Reineking, A.; Smedley, P. A.; Suckow, A.; Struijs, T.; Voors, P. I.; Yoshimiza, K.; Wyse, E. J. Radioanal. Nucl. Chem. 2007, 273, 383–393. (28) Pham, M. K.; Sanchez-Cabeza, J. A.; Povinec, P. P.; Andor, K.; Arnold, D.; Benmansour, M.; Bikit, I.; Carvalho, F. P.; Dimitrova, K.; Edrev, Z. H.; Engeler, C.; Fouche, F. J.; Garcia-Orellana, J.; Gascó, C.; Gastaud, J.; Gudelis, A.; Hancock, G.; Holm, E.; Legarda, F.; Ikäheimonen, T. K.; Ilchmann, C.; Jenkinson, A. V.; Kanisch, G.; Kis-Benedek, G.; Kleinschmidt, R.; Koukouliou, V.; Kuhar, B.; LaRosa, J.; Lee, S.-H.; LePetit, G.; Levy-Palomo, I.; Liong Wee Kwong, L.; Llauradó, M.; Maringer, F. J.; Meyer, M.; Michalik, B.; Michel, H.; Nies, H.; Nour, S.; Oh, J.-S.; Oregioni, B.; Palomares, J.; Pantelic, G.; Pfitzner, J.; Pilviok, R.; Puskeiler, L.; Satake, H.; Schikowski, J.; Vitorovic, G.; Woodhead, D.; Wyse, E. Appl. Radiat. Isot. 2008, 66, 1711– 1717. 6852 <strong>Analytical</strong> <strong>Chemistry</strong>, Vol. 82, No. 16, August 15, 2010 The IAEA-313, a stream sediment from Indonesia, 29 is a reference material designed for the analysis of 226Ra, U, and Th in geological samples. Its median 226Ra activity, 343 Bq kg-1 , is about 1 order of magnitude higher than typical sediment activities. The median value (N ) 5) is within the reported 95% confidence interval. The observed deviations are typical of the precision of environmental materials, and in overall, we concluded that the proposed method is adequate to analyze 226Ra in sediment samples. Calibration Stability. With each sample batch, we have analyzed the IAEA-384 reference material for quality control purposes. Results of all analyses are shown in Figure 10. The mean value, 2.3 Bq kg-1 , lies within the reference material 95% confidence interval (Table 3), and the time stability of the activity shows that the system’s calibration is stable for times spanning at least during the measurement period, namely, one year. Although this needs to be checked for each instrument in a continuous manner, we do not anticipate the need of recalibration of Quantulus 1220 for periods shorter than a year. 210 226 Pb and Ra in a Sediment Core. The method is designed to provide fast and reliable results of 226Ra when 210Pb dating sediment cores through the analysis of 210Po in equilibrium. The advantage of LSC over γ spectrometry is that results for a large number of samples, typical of 210Pb dating experiments, can be obtained within a month after sample digestion. We provide here an example of the proposed strategy. The DYFAMED station (Ligurian Sea, 43°25′ N; 7°52′ E) has been the subject of multidisciplinary research since 1987, including the study of atmospheric deposition of metals and their association with marine particles in the water column. Martín et al. 30 studied the concentrations and fluxes of trace metals in a sediment core collected from 2300 m water depth at the sea floor beneath the DYFAMED site. In Figure 11, we show the 210Pb and 226 Figure 9. Box-and-whisker plots of Ra profiles obtained by R spectrometry and LSC, showing that 226Ra activities in the reference material IAEA-384 (N ) 15). The two dots in the 50 channels counting window were statistically identified as outliers. (29) Strachnov, V.; Valkovic, V.; Zeisler, R.; Dekner, R. Report on the Worldwide Intercomparison Exercise IAEA-314: 226 Ra, Th and U in Stream Sediment; International Atomic Energy Agency (IAEA/AL/038): Vienna, Austria, 1991. (30) Martin, J.; Sanchez-Cabeza, J. A.; Eriksson, M.; Miquel, J. C. Mar. Pollut. Bull. 2009, 59, 146–153.
Table 3. Analysis of 226 Ra in Sediment Reference Materials (RM) reference material no. of analyses method median (Bq kg-1 ) RM median (Bq kg-1 ) RM 95% confidence interval deviation IAEA-384 15 2.2 2.4 2.0–2.9 -8.3 IAEA-385 15 23.5 21.9 21.6–22.4 +7.3 IAEA-313 5 372 343 307–379 +8.5 Figure 10. Time stability test for 226 Ra concentrations in the IAEA- 384 reference material. 226Ra reaches equilibrium in the core bottom sections. An important finding was that, although a constant 226Ra is commonly estimated from core bottom sections, where 210Pb and 226Ra are assumed to be in equilibrium, this is not the case in the DYFAMED core, where 226Ra ranged from 22.6 to 41.7 Bq kg-1 . This reinforces the need for paired 210Pb/ 226 Figure 11. Ra 210Pb and 226Ra profiles in a sediment core from the DYFAMED site (Ligurian Sea). measurements and methodologies to accomplish it accurately, as does the technique described in this paper. This may have important implications on the dating results for this particular sediment core, which will be discussed elsewhere. CONCLUSIONS The accurate 210 Pb dating of sediment cores requires the determination of 226 Ra in all sections. Although this can be done by γ spectrometry, the large sample size required (>5 g dry weight in well detectors, >20 g in coaxial detectors) might be impossible to obtain when sediments are used for the analysis of multiple magnitudes (such as grain size, elemental composition, trace metals, organic substances, biomarkers, ...) and counting times (typically >2 days per sample) might be a limiting factor for many laboratories. The proposed strategy in this work is the determination of 210 Pb through 210 Po in equilibrium by R spectrometry 10 followed by 226 Ra by LSC without any further radiochemical processing. We optimized the counting parameters for an ultralow background scintillation system with R-� separation capabilities (Quantulus 1220, Wallac) and propose the use of a PSA parameter of 145. The system was calibrated with a series of quenched 226 Ra standard solutions. For a typical sediment sample quenching (SQP(E) ) 850), the efficiency was (173 ± 12)% in the wide energy counting window (150 channels) due to the simultaneous counting of three radionuclides in equilibrium ( 222 Rn, 218 Po, and 214 Po). When analyzing 250 mg dw sediment samples, the MDA was as low as 0.29 Bq kg -1 , which is about 2 orders of magnitude lower than typical sediment concentrations, showing the usefulness of the technique for many other environmental applications. The method was validated with three reference materials spanning 3 orders of magnitude of concentration. The proposed method can greatly improve the reliability of 210 Pb chronologies of sediment cores, and can also be tested for 226 Ra/ 210 Pb dating of carbonates such as corals and speleothems. ACKNOWLEDGMENT The authors thank Mr. Jacobo Martín (IAEA) for providing samples of a sediment core from the DYFAMED site and helpful comments. The IAEA is grateful for the support provided to its Marine Environment Laboratories by the Government of the Principality of Monaco. Received for review March 31, 2010. Accepted June 30, 2010. AC1008332 <strong>Analytical</strong> <strong>Chemistry</strong>, Vol. 82, No. 16, August 15, 2010 6853
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Anal. Chem. 2010, 82, 6745-6750 Let
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purchased from Invitrogen-Molecular
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Figure 3. Electropherograms of TPP-
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Anal. Chem. 2010, 82, 6751-6755 Res
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(pH 8.0) with cysteine and cystamin
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Figure 4. Ion mobility mass spectra
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GOx glucose + O298 gluconic acid +
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coater at 2000 rpm for 20 s, and th
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Figure 5. Comparison of cyclic volt
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in channels with either no grooves
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indicators of atmospheric processin
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Figure 1. GC/MS total ion chromatog
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Table 2. Concentrations and Stable
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on a substrate are preferred. 20-24
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Figure 4. SERS analysis of NAADP co
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Anal. Chem. 2010, 82, 6775-6781 Hig
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tion, 2 µL of proprionaldehyde wer
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Figure 4. Analysis of 2a by HPLC-MS
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eaction of 1a with PBH can be condu
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Numerous references had demonstrate
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Figure 1. TEM images of the prepare
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Figure 4. Schematic representation
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esult in a big SPR signal change wi
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also reduces chemical noise, which
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Table 1. Extraction Yields, Liquid
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scanning of AMPP amides of the anal
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Anal. Chem. 2010, 82, 6797-6806 δ
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Figure 1. Schematic view of the pre
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ascorbic acid (AA), uric acid (UA),
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the multielement capabilities, the
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RESULTS AND DISCUSSION Sulfur Detec
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Table 2. Molecular Properties and C
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Anal. Chem. 2010, 82, 6911-6918 Dir
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dilution and hybridization buffer.
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solution under appropriate incubati
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Figure 4. Standardization curve for
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Anal. Chem. 2010, 82, 6919-6925 Ele
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the ×10 objective, to have a large
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Figure 2. With a suitable removal o
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the NB signal in a much better foot
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Scheme 1. Reactions of Selenium Rea
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Figure 2. (a) ESI-MS spectrum showi
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Figure 4. (a) ESI-MS spectrum showi
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Anal. Chem. 2010, 82, 6933-6939 Dif
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trode 28 by a finite element using
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Figure 4. Comparison between simula
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Figure 6. Comparison between simula
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educed in the vicinity of double bo
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Figure 2. Normalized product ion ab
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Figure 4. EID (a) and IRMPD (b) of
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Anal. Chem. 2010, 82, 6947-6957 Ide
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Figure 1. Schematic flowchart showi
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difference, ppm compound Table 1. I
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isoforms, its successful use, in th
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Figure 5. Extracted ion current ESI
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m/z 1172.935 was observed for Ser14
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linked products via affinity tags.
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Scheme 2. Fragmentation Mechanism o
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Figure 1. (A) ESI-LTQ-CID-MS 2 prod
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Figure 3. (A) ESI-LTQ-CID-MS 2 prod
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Figure 5. (A) MALDI-TOF/TOF product
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Anal. Chem. 2010, 82, 6969-6975 Ana
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Figure 3. Equilibrium response as a
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Figure 6. The average measured resp
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for the fill time, and we find that
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nucleotide tails. 3-5 Thus, the amo
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allow the use of higher aptamer con
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quent ligation of the aptamers afte
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Anal. Chem. 2010, 82, 6983-6990 Imp
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Figure 2. Configuration editor wind
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Figure 4. Dependencies between volu
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Since the time for liquid expulsion
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Anal. Chem. 2010, 82, 6991-6999 Int
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Figure 1. Representation of the Car
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Table 2. Capillary Electrophoresis
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Figure 4. (A) Typical raw electroph
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field. DNA profiles were delivered
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Another approach to handle this lim
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(principal components, PCs) in whic
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Figure 5. Relevant score plots and
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CONCLUSIONS In this paper we have i
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electroactive-species loaded liposo
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Figure 2. Qdot-based FLFTS response
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Figure 6. Fluorescence imaging of Q
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Anal. Chem. 2010, 82, 7015-7020 Sel
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Table 1. Effect of 1 D-LC Condition
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Figure 3. Peak-production rate vers
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Anal. Chem. 2010, 82, 7021-7026 Cel
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luciferase (T7 control vector) was
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Figure 3. Inhibitory effects of luc
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Anal. Chem. 2010, 82, 7027-7034 Pat
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Electrochemistry. Electrochemical m
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Figure 2. SEM images of Au substrat
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Table 3. Film Thickness Measurement
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Anal. Chem. 2010, 82, 7035-7043 Qua
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Figure 1. (A) FL spectra of BSPOTPE
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Figure 4. (A) Variation in the FL i
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Figure 6. (A) FL spectra of BSPOTPE
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Scheme 1. Proposed Mechanism for Fl
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one or more drawbacks including poo
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Figure 2. Free fluorophores do not
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Anal. Chem. 2010, 82, 7049-7052 Dev
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Figure 2. Comparative analysis of d