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. Author manuscript; available in PMC: 2014 Aug 7.
Published in final edited form as: J Agric Food Chem. 2011 Oct;59(19):10773. doi: 10.1021/jf203649c

Addition to determination of parent and substituted polcyclic aromatic hydrocarbons in high-fat salmon using a modified QuEChERS extraction, dispersive SPE and GC-MS

Norman D Forsberg 1, Glenn R Wilson 1, Kim A Anderson 1,*
PMCID: PMC4124910  NIHMSID: NIHMS473847

Subsequent to our reported results, we found that the d-SPE materials prescribed for our modified QuEChERS extraction method display lot-to-lot PAH contamination (Figure 1). Whereas some lots of d-SPE material showed substantial amounts of PAH contamination (Lot B), others displayed very little (Lot C) or none at all (Lot A). Identified PAH contaminants included naphthalene, 1-methyl naphthalene, 2-methyl naphthalene, fluoranthene, pyrene and benzo(g,h,i)perylene. Average levels of contamination ranged from 126 to 2 pg/uL for naphthalene and benzo(g,h,i)perylene respectively and decreased in the order naphthalene > pyrene > 2-methyl naphthalene > 1-methyl naphthalene > benzo(g,h,i)perylene. In light of this finding, we characterized the variability of PAH contamination through replicate analyses of the d-SPE tubes and incorporated these findings into new MDL estimates (Table 1). We suggest that researchers seeking to employ this method either use the updated MDLs presented herein or analyze their d-SPE materials for PAH contamination and incorporate findings into their reporting limits.

Figure 1.

Figure 1

PAH contamination levels in different lots of fatty sample d-SPE materials

Table 1.

Method detection limits that account for fatty sample d-SPE PAH contamination

PAH Modified QuEChERS MDL (ug/g)
Naphthalene 0.156
2-Methylnaphthalene 0.041
1-Methylnaphthalene 0.016
Fluoranthene 0.021
Pyrene 0.078
Benzo[g,h,i]perylene 0.012

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