Sentence examples for furnace absorption from inspiring English sources

Blood specimens were analyzed for lead at the NHANES Laboratory, Division of Environmental Health Laboratory Sciences, National Center for Environmental Health, CDC, using graphite furnace absorption spectrophotometry and previously described methods (Gunter et al. 1996).

Trace amounts of Cr, Zn, Cd, and Pb were determined by metal furnace atomic absorption spectrometry using absorption tubes.

We determined blood lead concentration by graphite furnace atomic absorption spectrophotometry (Miller et al. 1987; Parsons and Slavin 1993).

Plasma selenium concentration was determined using graphite furnace atomic absorption spectrophotometry with Zeeman background correction.

Blood lead concentration was measured by graphite furnace atomic absorption spectrometry (GFAAS) with Zeeman background correction.

Plasma selenium concentration was determined using graphite furnace atomic absorption spectrophotometry.

34 35 Total arsenic concentration was determined by graphite furnace atomic absorption spectrometry with a Hitachi Z-8200 system.

Blood lead concentration was determined by graphite furnace atomic absorption spectrophotometry (Miller et al. 1987; Parsons and Slavin 1993).

Serum Se concentration was analysed by graphite furnace atomic absorption spectroscopy (GFAAS, SOLAAR M, Thermo Fisher Scientific, Dreieich, Germany).

Total arsenic concentration was measured by graphite furnace atomic absorption, using a PerkinElmer AAnalyst 600 graphite furnace system (PerkinElmer, Waltham, MA, USA) with a detection limit of 2 μg/L, as previously described (Nixon et al. 1991).

Total urinary arsenic concentration was measured by graphite furnace atomic absorption spectrometry using a Perkin-Elmer AAnalyst 600 graphite furnace system (PerkinElmer, Wellesley, MA) in the Columbia University Trace Metals Core Laboratory, as described previously (Nixon et al. 1991).