Determination of As(III) in nonacidified groundwater samples for inorganic speciation analysis using flow injection hydride generation atomic absorption spectrometry

A flow injection system coupled to hydride generation atomic absorption spectrometry with heated quartz tube atomizer was employed for the selective determination of As(III) in real groundwater samples under nonacidic conditions. The use of low-acidity conditions was carefully evaluated in order to...

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Autor principal: Sigrist, M.
Otros Autores: Beldoménico, H., Tudino, M.
Formato: Capítulo de libro
Lenguaje:Inglés
Publicado: 2010
Acceso en línea:Registro en Scopus
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100 1 |a Sigrist, M. 
245 1 0 |a Determination of As(III) in nonacidified groundwater samples for inorganic speciation analysis using flow injection hydride generation atomic absorption spectrometry 
260 |c 2010 
270 1 0 |m Sigrist, M.; Laboratorio Central, Facultad de Ingeniería Química, Universidad Nacional del Litoral, Santiago del Estero 2654-Piso 6, Santa Fe, 3000, Argentina; email: msigrist@fiq.unl.edu.ar 
506 |2 openaire  |e Política editorial 
504 |a Dedina, J., Tsalev, D., (1995) Hydride Generation Atomic Absorption Spectrometry, , Wiley & Sons: Chichester, U.K 
504 |a Braman, R., Johnson, D., Foreback, C., Ammons, J., Bricker. Separation and determination of nanogram amounts of inorganic arsenic and methylarsenic compounds (1977) J. Anal. Chem, 49, p. 621 
504 |a Anderson, R., Thompson, M., Culbard, E., Selective reduction of arsenic species by continuous hydride generation. Part I. Reaction media (1986) Analyst, 111, p. 1143 
504 |a Hall, G., Pelchat, J., Gauthier, G., Stability of inorganic arsenic (III) and arsenic (V) in water samples (1999) J. Anal. At. Spectrom, 14, p. 205 
504 |a D́Ulivo, A., Determination of the deuterium=hydrogen ratio in gas reaction products by laser-induced breakdown spectroscopy (2006) Spectrochim. Acta, Part B, 61, p. 797 
504 |a D́Ulivo, A., Mester, Z., Meija, J., Sturgeon, R.E., Mechanism of generation of volatile hydrides of tracs Elements by Aqueous tetrahydroborate (III) (2007) Anal. Chem, 79, p. 3008 
504 |a D́Ulivo, A., Baiocchi, C., Pitzalis, E., Onor, M., Zamboni, R., Chemical vapor generation for atomic spectroscopy. A contribution to the comprehension of reaction mechanisms in the generation of volatile hydrides using borane complexes (2004) Spectrochim. Acta, Part B, 59, p. 471 
504 |a Dedina, J., Atomization of volatile compounds for atomic absorption and atomic fluorescence spectrometry: On the way towards the ideal atomizer (2007) Spectrochim. Acta, Part B, 62, p. 846 
504 |a Welz, B., Guo, T., Formation and interpretation of double peaks in flow injection hydride generation atomic absorption spectrometry (1992) Spectrochim. Acta, Part B, 47, p. 645 
504 |a Welz, B., Melcher, M., Investigation on atomisation mechanisms of volatile hybride-forming elements in a heated quartz cell. Part 1. Gas-phase and surface effects; decomposition and atomisation of arsine (1983) Analyst, 108, p. 213 
504 |a Dedina, J., Welz, B., Quartz tube atomizers for hybride-generation (1992) J. Anal. At. Spectrom, 7, p. 307 
504 |a Welz, B., Sucmanova, M., 1-Cysteine as a reducing and releasing agent for the determination of antimony and arsenic using flow injection hydride generation atomic absorbtion spectrometry. Part 1 (1993) Analyst, 118, p. 1417 
504 |a Nielsen, S., Hansen, E., Determination of As(III) and As(V) by flow injection-hydride generation-atomic absorption spectrometry via on-line reduction of As(V) by KI (1997) Analytica Chimica Acta, 343, p. 5 
520 3 |a A flow injection system coupled to hydride generation atomic absorption spectrometry with heated quartz tube atomizer was employed for the selective determination of As(III) in real groundwater samples under nonacidic conditions. The use of low-acidity conditions was carefully evaluated in order to minimize the interconversion of redox arsenic species. The As(III) hydride was generated using 0.1 mol L-1 HCl as carrier solution and 0.2% (m/v) NaBH4 in 0.025% NaOH as the reductant. A coil reaction larger than the used one for higher acidity conditions (480 mm instead of 115 mm) was selected. The generated hydride was transported to the atomizer by a nitrogen flow of 75 ml min-1. The main parameters that influenced the signal intensity and shape were studied. Under the best found experimental conditions, a detection limit (3σ) of 1.0 μgL-1 As(III) was obtained for a 500 μl sample volume. The analytical recovery ranged between 90% and 98%. In addition, the total inorganic arsenic concentration in the samples was determined on sample aliquots acidified with concentrated HCl and prereduced with 5% (m/v) KI-5% (m/v) C6H8O6 solution. HCl 1.2 mol L-1 as carrier solution, NaBH4 0.2% (m/v) as reductant, and a nitrogen flow rate of 75 ml min-1 were used in this case. The concentration of As(V) was calculated by difference between the total inorganic arsenic and As(III) concentrations. © Taylor & Francis Group, LLC.  |l eng 
593 |a Laboratorio Central, Facultad de Ingeniería Química, Universidad Nacional del Litoral, Santiago del Estero 2654-Piso 6, Santa Fe, 3000, Argentina 
593 |a Laboratorio de Análisis de Trazas, Departamento de Química Inorgánica, Analítica y Química Física, Facultad de Ciencias Exactas y Naturales, Ciudad Universitaria, Buenos Aires, Argentina 
690 1 0 |a ARSENIC SPECIATION 
690 1 0 |a ATOMIC ABSORPTION SPECTROMETRY 
690 1 0 |a FLOW INJECTION 
690 1 0 |a HYDRIDE GENERATION 
690 1 0 |a NONACIDIFIED WATER SAMPLES 
700 1 |a Beldoménico, H. 
700 1 |a Tudino, M. 
773 0 |d 2010  |g v. 43  |h pp. 458-464  |k n. 6  |p Spectrosc. Lett.  |x 00387010  |w (AR-BaUEN)CENRE-6903  |t Spectroscopy Letters 
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856 4 0 |u https://doi.org/10.1080/00387010903261214  |y DOI 
856 4 0 |u https://hdl.handle.net/20.500.12110/paper_00387010_v43_n6_p458_Sigrist  |y Handle 
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