J P Oliveira1, M E de Siqueira, C S da Silva. 1. Escola de Farmacia e Odontologia de Alfenas, Departamento de Análises Clínicas, Alfenas, Brazil. marelisa@int.efoa.br
Abstract
OBJECTIVES: We measured urinary nickel (U-Ni) in ten workers (97 samples) from a galvanizing plant that uses nickel sulfate, and in ten control subjects (55 samples) to examine the association between occupational exposure to airborne Ni and Ni absorption. METHODS: Samples from the exposed group were taken before and after the work shift on 5 successive workdays. At the same time airborne Ni (A-Ni) was measured using personal samplers. Ni levels in biological material and in the airborne were determined by a graphite furnace atomic absorption spectrometry validated method. In the control group the urine samples were collected twice a day, in the before and after the work shift, on 3 successive days. RESULTS: Ni exposure low to moderate was detected in all the examined places in the plant, the airborne levels varying between 2.8 and 116.7 micrograms/m3 and the urine levels, from samples taken postshift, between 4.5 and 43.2 micrograms/g creatinine (mean 14.7 micrograms/g creatinine). Significant differences in U-Ni creatinine were seen between the exposed and control groups (Student's t test, P < or = 0.01). A significant correlation between U-Ni and A-Ni (r = 0.96; P < or = 0.001) was detected. No statistical difference was observed in U-Ni collected from exposed workers in the 5 successive days, but significant difference was observed between pre- and postshift samples. CONCLUSIONS: Urinary nickel may be used as a reliable internal dose bioindicator in biological monitoring of workers exposed to Ni sulfate in galvanizing plants regardless of the day of the workweek on which the samples are collected.
OBJECTIVES: We measured urinary nickel (U-Ni) in ten workers (97 samples) from a galvanizing plant that uses nickel sulfate, and in ten control subjects (55 samples) to examine the association between occupational exposure to airborne Ni and Ni absorption. METHODS: Samples from the exposed group were taken before and after the work shift on 5 successive workdays. At the same time airborne Ni (A-Ni) was measured using personal samplers. Ni levels in biological material and in the airborne were determined by a graphite furnace atomic absorption spectrometry validated method. In the control group the urine samples were collected twice a day, in the before and after the work shift, on 3 successive days. RESULTS: Ni exposure low to moderate was detected in all the examined places in the plant, the airborne levels varying between 2.8 and 116.7 micrograms/m3 and the urine levels, from samples taken postshift, between 4.5 and 43.2 micrograms/g creatinine (mean 14.7 micrograms/g creatinine). Significant differences in U-Ni creatinine were seen between the exposed and control groups (Student's t test, P < or = 0.01). A significant correlation between U-Ni and A-Ni (r = 0.96; P < or = 0.001) was detected. No statistical difference was observed in U-Ni collected from exposed workers in the 5 successive days, but significant difference was observed between pre- and postshift samples. CONCLUSIONS: Urinary nickel may be used as a reliable internal dose bioindicator in biological monitoring of workers exposed to Ni sulfate in galvanizing plants regardless of the day of the workweek on which the samples are collected.
Authors: Adriana Arita; Alexandra Muñoz; Yana Chervona; Jingping Niu; Qingshan Qu; Najuan Zhao; Ye Ruan; Kathrin Kiok; Thomas Kluz; Hong Sun; Hailey A Clancy; Magdy Shamy; Max Costa Journal: Cancer Epidemiol Biomarkers Prev Date: 2012-11-29 Impact factor: 4.254
Authors: Adriana Arita; Jingping Niu; Qingshan Qu; Najuan Zhao; Ye Ruan; Arthur Nadas; Yana Chervona; Fen Wu; Hong Sun; Richard B Hayes; Max Costa Journal: Environ Health Perspect Date: 2011-10-24 Impact factor: 9.031