Environmental Health Criteria 214
Environmental Health Criteria 214
Environmental Health Criteria 214
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HUMAN EXPOSURE ASSESSMENT<br />
A specific example for an approach used in external QC is the<br />
UNEP/WHO regression method. The regression method is based on the QC<br />
programmes developed in the UNEP/WHO pilot project on assessment of<br />
human exposure to pollutants through biological monitoring for the<br />
determination of lead in blood and cadmium in kidney cortex (Vahter,<br />
1982). This external QC method was also applied in the UNEP/WHO Human<br />
Exposure Assessment Location (HEAL) study. For the studies on lead and<br />
cadmium, reference external QC samples of blood, air filter material,<br />
dust and diet were sent to participating laboratories (Vahter &<br />
Slorach, 1990). The same procedure was also adopted for the HEAL<br />
nitrogen dioxide study, using standard sodium nitrite solutions and<br />
nitrogen dioxide-exposed sample badges as QC samples (Matsushita &<br />
Tanabe, 1991).<br />
Table 37. External QC schemes<br />
Scheme Country Reference<br />
Centre de Toxicologie du Quebec Canada Weber, 1988<br />
(CTQ)<br />
Danish External Quality Assessment Denmark Anglov et al.,<br />
Scheme (DEQAS) 1993<br />
External quality control in the Germany Schaller, 1991<br />
toxicological analyses of biological<br />
materials, German Society of<br />
Occupational Medicine<br />
Japanese External Quality Japan Sugita et al.,<br />
Assessment Scheme 1990<br />
NIOSH Proficiency Analytical USA NIOSH, 1979<br />
Testing Programme<br />
United Kingdom National External United UKNEQAS, 1993;<br />
Quality Assessment Schemes Kingdom Bullock, 1986<br />
(UKQAS)<br />
The accuracy and precision of the analytical results were<br />
evaluated by using a statistical technique known as the maximum<br />
allowable deviations (MAD) method (Vahter, 1982; WHO, 1986; UNEP/WHO,<br />
1991). This method is based on the linear regression line of reported<br />
versus "true" values and established acceptance criterion on how much<br />
the line may deviate from the ideal line where the measured equals the<br />
expected value. Acceptance criteria or the MADs have to be decided on<br />
separately for each pollutant or for each medium. The stringency of<br />
the MAD is primarily based on the required quality of the actual<br />
monitoring data and the sensitivity, accuracy and precision of the<br />
analytical methods. As in the use of control charts, decision<br />
concerning acceptance and rejection of results is based on statistical<br />
criteria, i.e., on the probability of making right or wrong decisions.<br />
A laboratory may be erroneously rejected when in fact its methodology<br />
is satisfactory, or it may be erroneously accepted when its<br />
methodology is not satisfactory. Power analysis is done to determine<br />
the probability of including an unsatisfactory laboratory. The concept<br />
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