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Samples are therefore usually prepared and positioned to minimise the influence of other variables.
The optical indices, n and k, of the various samples are therefore needed for these two wavelengths.
After growth, the samples are therefore constituted of a silicon substrate with an AAO template filled with silicon nanowires.
(GCtimes GC) topographies for same-source injections from different samples are therefore, bound to exhibit more variation due to shifting of minor peaks, co-elution of different biomarkers, as well as baseline variability.
This is in a good agreement with the estimate of instrumental uncertainty Δh of the adjustable gap thickness h, given in Table 3. Possible slip effects in all the studied samples are therefore quite negligible in comparison with the instrumental uncertainty.
Different numbers of samples are therefore reported for the different loci.
Similar(46)
A rectangular sliding window of 128 samples was therefore used.
These samples were therefore classified as tidal channel October samples in the analyses (Table 2).
The vast majority of HS in the sorption samples was therefore partitioned to the solid phase.
Wastewater samples were therefore not necessarily the most toxic when their fractions exhibited the highest inhibitory effects.
Duplicate samples were therefore taken from the larger iceberg samples (S1, S4, KG1 and KG2) to provide a rough estimate of sampling variations.
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