Air exposure assessment and biological monitoring of manganese and other major welding fume components in welders

被引:63
作者
Ellingsen, Dag G.
Dubeikovskaya, Larisa
Dahl, Kari
Chashchin, Maxim
Chashchin, Valery
Zibarev, Evgeny
Thomassen, Yngvar
机构
[1] Natl Inst Occupat Hlth, N-0033 Oslo, Norway
[2] NW Publ Hlth Res Ctr, St Petersburg 191036, Russia
来源
JOURNAL OF ENVIRONMENTAL MONITORING | 2006年 / 8卷 / 10期
关键词
D O I
10.1039/b605549d
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
In a cross-sectional study, 96 welders were compared with 96 control subjects. Also 27 former welders, all diagnosed as having manganism, were examined. Exposure to welding fumes was determined in the 96 welders, while the concentration of elements in whole blood and urine was determined in all subjects. The geometric mean ( GM) concentrations of manganese ( Mn) and iron in the workroom air were 97 mu g m(-3) ( range 3-4620 mu g m(-3); n = 188) and 894 mu g m(-3) ( range 106-20 300 mu g m(-3); n = 188), respectively. Thus the Mn concentration in the workroom air was on average 10.6% ( GM) of that of the Fe concentration. No substantial difference was observed in the air Mn concentrations when welding mild steel as compared to welding stainless steel. The arithmetic mean ( AM) concentration of Mn in whole blood ( B-Mn) was about 25% higher in the welders compared to the controls ( 8.6 vs. 6.9 mg l(-1); p < 0.001), while the difference in the urinary Mn concentrations did not attain statistical significance. A Pearson's correlation coefficient of 0.31 ( p < 0.01) was calculated between B-Mn and Mn in the workroom air that was collected the day before blood sampling. Although the exposure to welding fumes in the patients had ceased on average 5.8 years prior to the study ( range 4 years-7 years), their AM B-Mn concentration was still higher than in referents of similar age ( 8.7 mu g l(-1) vs. 7.0 mg l(-1)). However, their urinary concentrations of cobolt, iron and Mn were all statistically significantly lower.
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页码:1078 / 1086
页数:9
相关论文
共 43 条
[1]   EXPOSURE IN WELDING OF HIGH NICKEL-ALLOY [J].
AKESSON, B ;
SKERFVING, S .
INTERNATIONAL ARCHIVES OF OCCUPATIONAL AND ENVIRONMENTAL HEALTH, 1985, 56 (02) :111-117
[2]   Pulmonary responses to welding fumes: Role of metal constituents [J].
Antonini, JM ;
Taylor, MD ;
Zimmer, AT ;
Roberts, JR .
JOURNAL OF TOXICOLOGY AND ENVIRONMENTAL HEALTH-PART A-CURRENT ISSUES, 2004, 67 (03) :233-249
[3]   Health effects of welding [J].
Antonini, JM .
CRITICAL REVIEWS IN TOXICOLOGY, 2003, 33 (01) :61-103
[4]  
Apostoli P, 2000, AM J IND MED, V37, P283, DOI 10.1002/(SICI)1097-0274(200003)37:3<283::AID-AJIM6>3.3.CO
[5]  
2-5
[6]   Expression of the iron transporter DMT1 in kidney from normal and anemic mk mice [J].
Canonne-Hergaux, FS ;
Gros, P .
KIDNEY INTERNATIONAL, 2002, 62 (01) :147-156
[7]   AN EXPLORATORY-STUDY OF MANGANESE EXPOSURE TO WELDERS [J].
CHANDRA, SV ;
SHUKLA, GS ;
SRIVASTAVA, RS ;
SINGH, H ;
GUPTA, VP .
CLINICAL TOXICOLOGY, 1981, 18 (04) :407-416
[8]   CHRONIC MANGANESE POISONING - CLEARANCE OF TISSUE MANGANESE CONCENTRATIONS WITH PERSISTENCE OF NEUROLOGICAL PICTURE [J].
COTZIAS, GC ;
HORIUCHI, K ;
FUENZALIDA, S ;
MENA, I .
NEUROLOGY, 1968, 18 (04) :376-+
[9]  
Doherty MJ, 2004, OCCUP ENVIRON MED, V61, P82
[10]   PULMONARY CLEARANCE OF SOLUBLE AND INSOLUBLE FORMS OF MANGANESE [J].
DROWN, DB ;
OBERG, SG ;
SHARMA, RP .
JOURNAL OF TOXICOLOGY AND ENVIRONMENTAL HEALTH, 1986, 17 (2-3) :201-212