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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 />

http://www.inchem.org/documents/ehc/ehc/ehc<strong>214</strong>.htm<br />

Page 196 of 284<br />

6/1/2007

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