99
98
95
90
70
50
30
10
5
2
0.1
1.0
4.0
QC
a. Ethylbenzene.
Ethylbenzene
Concentration Ratios
QA
99
98
95
90
70
50
30
10
5
2
0.1
1.0
10
QC
b. Toluene.
Toluene
Concentration Ratios
QA
Figure 6. Lognormal probability plots for QC/QA concentration ratios for soil VOCs.
likely we are to experience biases and the more
and, therefore, they omit all error associated with
difficult it becomes to identify them.
sample collection, transport, storage, and extrac-
What about the QC results from matrix spike/
tion. Assuming that the solution used for spiking
matrix spike duplicates (MS/MSD)? We could find
is prepared independently from the calibration
no meaningful correlation between these results
standards (frequently untrue), MS/MSD results
and the degree of agreement between QC and
QA laboratories. Similar failure of MS/MSD re-
sults as a quality indicator for VOCs was recently
reported by Robertson et al. (1995). Generally
contribute to the disagreement between laborato-
speaking, the MS/MSD results appeared to be
ries? The answer is no. Significant bias may be
quite satisfactory and suggestive of much greater
introduced from calibration errors, but we do not
believe it is the major source of error. In contrast
cated samples. However, we must remember that
to the soil results, we found that most QC/QA
MS/MSD results are derived by spiking extracts
ratios for GC-MS determination of VOCs in
10