A comparison of X-ray fluorescence and wet chemical analysis for lead on air filters from different personal samplers used in a bronze foundry

被引:16
作者
Harper, M
Pacolay, B
Andrew, ME
机构
[1] NIOSH, Exposure Assessment Branch, Hlth Effects Lab Div, Morgantown, WV 26505 USA
[2] NIOSH, Biostat Branch, Hlth Effects Lab Div, Morgantown, WV 26505 USA
来源
JOURNAL OF ENVIRONMENTAL MONITORING | 2005年 / 7卷 / 06期
关键词
D O I
10.1039/b502170g
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
Portable X-ray fluorescence (XRF) technology may provide faster turn-around without compromising accuracy when assessing personal exposures to metals such as lead, but it has only been tested in limited field environments. This study is part of a series, where different sampler types are used to collect airborne lead in different environments for presentation to a portable XRF analyzer. In this case personal samples were taken at a bronze foundry where lead is added to an alloy of copper, zinc and iron to improve casting, using the closed-face 37 mm cassette, the 37 mm GSP or "cone" sampler, the 25 mm Institute of Occupational Medicine (IOM) inhalable sampler, the 25 mm Button sampler, and the open-face 25 mm cassette. Mixed cellulose-ester filters were used in all samplers. Following XRF analysis the samples were extracted with acid and analyzed by inductively coupled plasma optical emission spectroscopy (ICP). For lead, all five samplers gave correlations (r(2)) greater than 0.9 between the two analytical methods over the entire range of found lead mass, which encompassed both the action level and the permissible exposure limit enforced in the USA by the Occupational Safety and Health Administration (OSHA). However, a correction was required to adjust linear regression trendlines to give a 1 : 1 correlation for the average of three readings across the GSP sampler, and a similar correction was required for the single readings from the IOM sampler and the 25 mm filter cassette. The bias possibly is due to interference from other metals, possibly copper which can absorb the fluorescent radiation of lead. In the case of the Button sampler, the bias is larger, indicating a further source of error, perhaps due to the thickness of the deposit. However, in all cases, correction of the lead results did not greatly affect the overall percentage of samples where the XRF result was within 25% of the ICP result, although it did improve the overall accuracy of the results. The GSP, IOM and Button samplers are suitable candidates for further evaluation as compatible with on-site XRF analysis for lead and other metals. It is important to check carefully factory pre-set instrument calibrations, as a bias in the calibration for copper was observed.
引用
收藏
页码:592 / 597
页数:6
相关论文
共 15 条
[1]   Performance characteristics of the button personal inhalable aerosol sampler [J].
Aizenberg, V ;
Grinshpun, SA ;
Willeke, K ;
Smith, J ;
Baron, PA .
AMERICAN INDUSTRIAL HYGIENE ASSOCIATION JOURNAL, 2000, 61 (03) :398-404
[2]   Evaluation of two portable lead-monitoring methods at mining sites [J].
Drake, PL ;
Lawryk, NJ ;
Ashley, K ;
Sussell, AL ;
Hazelwood, KJ ;
Song, RG .
JOURNAL OF HAZARDOUS MATERIALS, 2003, 102 (01) :29-38
[3]  
ELLER P, 1994, PUBLICATION NIOSH S
[4]  
ELLER PM, 1994, PUBLICATION NIOSH
[5]  
ELSKAMP CJ, 2003, OSHA MANUAL ANAL MET
[6]  
*EN, 1994, 482 EN COM EUR NORM
[7]  
HARPER M, 1987, BRIT J IND MED, V44, P652
[8]   A comparison of X-ray fluorescence and wet chemical analysis of air filter samples from a scrap lead smelting operation [J].
Harper, M ;
Hallmark, TS ;
Andrew, ME ;
Bird, AJ .
JOURNAL OF ENVIRONMENTAL MONITORING, 2004, 6 (10) :819-826
[9]  
*HLTH SAF EX, 1987, 7 MDHS HLTH SAF EX
[10]   NEW AEROSOL SAMPLER WITH LOW WIND SENSITIVITY AND GOOD FILTER COLLECTION UNIFORMITY [J].
KALATOOR, S ;
GRINSHPUN, SA ;
WILLEKE, K .
ATMOSPHERIC ENVIRONMENT, 1995, 29 (10) :1105-1112