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Y H Hwang

Publications and source records attributed to Y H Hwang.

40 records · Page 3Linked to original sources

Monitoring of low level arsenic exposure during maintenance of ion implanters.

To delineate potential exposure in ion implanter maintenance, the authors recruited 21 maintenance engineers (exposed group) and 10 computer programmers (controls) at three semiconductor manufacturing facilities. Samples of air, wipes, and urine; used cleaning cloths; and used gloves were collected for the characterization of arsenic exposure. Arsenic levels were very low in environmental samples, but high arsenic levels were found in some wipe samples, used cleaning cloths, and gloves. The average baseline content of urinary arsenic measured for maintenance engineers was 3.6 microg/g creatinine. Maintenance engineers experienced an increase of 1.0-7.8 microg/g creatinine in urinary arsenic levels during ion implanter maintenance. Results of a mixed-model analysis indicated that urinary arsenic levels were associated significantly with time series (p = .0001), and the extent of association was different among the three facilities (p = .0226). The results of this study indicate that arsenic intake via ingestion, rather than through inhalation, might play a significant role in the elevation of urinary arsenic levels. However, a series of urine samples with self-reference continue to be a good approach for the monitoring of low-level arsenic exposure.

Adult↗

Temporal fluctuation of the lead level in the cord blood of neonates in Taipei.

From August 1985 to September 1987, 9,502 cord blood samples were obtained from the Taipei Municipal Maternal and Child Hospital. A total of 205 cord blood samples chosen randomly from newborns without parental exposure to lead were analyzed by flameless atomic absorption spectrophotometry. The average blood lead level was .36 +/- .11 mumol/l (7.48 +/- 2.25 micrograms/dl). A similar analysis was performed on samples obtained from 160 newborns whose fathers had occupational lead exposure. In both groups, the average concentration of lead in cord blood in the summer was statistically greater than that in the winter. Air lead and total amount of lead in gasoline consumed in Taipei appeared to be associated with this seasonal fluctuation in the average lead level of cord blood. After considering alternative sources, we conclude that the seasonal fluctuation of cord blood lead is probably influenced by air lead produced from the combustion of gasoline.

Air Pollutants↗

Urinary arsenic excretion as a biomarker of arsenic exposure in children.

Urinary arsenic concentration has been used generally for the determination of exposure, but much concern has been raised over the most appropriate expression for urinary arsenic levels. In this study, we examined the influence of various adjustments of expressing urinary arsenic data. All children who were less than 72 mo of age and who were potty trained were invited to participate in the present study. Urine, soil, and dust samples were collected, and arsenic measurements were made. The geometric mean of speciated urinary arsenic among children who provided first-voided urine samples on 2 consecutive mornings was 8.6 microg/l (geometric standard deviation = 1.7, n = 289). Speciated urinary arsenic was related significantly to soil arsenic in bare areas (p < .0005). Use of a single urine sample versus the average of two first-voided urine samples collected on 2 consecutive mornings did not significantly alter the relationship between environmental arsenic and urinary arsenic levels. Furthermore, none of the adjustments to urinary concentration improved the strength of correlation between urinary arsenic and soil arsenic levels. Concentration adjustments may not be necessary for urinary arsenic levels obtained from young children who provide first-void samples in the morning.

Arsenic↗

Lip lead as an alternative measure for lead exposure assessment of lead battery assembly workers.

This study investigated lead exposures of lead battery assembly workers in Taiwan. A special attempt was made to evaluate the use of lip lead as an alternative index for occupational lead exposure. Ninety-six of 113 workers from a lead battery plant were recruited as study subjects. Air lead; lead loadings on workers' sleeves, gloves, hands, cheeks, and lips; and blood lead were determined for exposure assessment. A questionnaire also was administered to collect information on work history, suspected exogenous lead sources, and personal behavior and activities. Geometric means of total air lead at different subareas ranged from 0.070 (2.5 geometric standard deviation [GSD]) to 0.159 (1.8 GSD) mg/m3. Geometric means of respirable air lead level for different subgroups of workers varied from 0.009 (2.0 GSD) to 0.032 (1.9 GSD) mg/m3, whereas those of the blood lead level ranged from 22.4 (1.3 GSD) to 44.5 (1.3 GSD) microg/dL. The heaviest lead loadings were found for plate-processing workers (e.g., 66.4 [1.5 GSD] on gloves, 0.80 [3.7 GSD] on cheeks, and 0.79 [3.2 GSD] microg/cm2) on bare-hands after washing. Blood lead level was significantly correlated with lead levels in air, lead loadings on lips, and bare hands after washing (r=0.24-0.30). Results of multiple regression analysis showed that only lip lead had a significant effect on the blood lead, whereas respirable air lead and personal behavior had only mild effects in this model. It was concluded that lip lead level may be used as an alternative index of lead exposure to facilitate the estimation of lead uptake through ingestion.

Cheek↗