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478 

M

astovska

et al

.

:

J

ournal of

AOAC I

nternational

V

ol

. 98, N

o

. 2, 2015

aromatic hydrocarbons (PAHs) in seafood. The primary goal

was to significantly reduce the time-to-signal (including sample

preparation and extraction) in comparison with currently

accepted analytical methods requiring 96–120 hours to

complete. In addition, acceptable methods had to demonstrate

an LOQ of 1 µg/kg for benzo[

a

]pyrene (BaP) in seafood. The

SPSC PAH Working Group on Quantitative Methods evaluated

about 30 methods that were submitted as a response to the

call or found in the literature. The evaluation criteria included:

fitness-for-purpose requirements (LOQ, speed, and scope),

identification and quantification (compatibility with MS), quality

of data to meet AOAC INTERNATIONAL single-laboratory

validation requirements (e.g., accuracy, precision, and analysis

of reference materials), and practical considerations, such as

availability of equipment.

The Working Group selected a method developed for the

determination of PAHs, polychlorinated biphenyls (PCBs), and

polybrominated diphenyl ethers (PBDEs) in fish and seafood by

Jana Hajslova’s group at the Institute of Chemical Technology

(ICT) in Prague, Czech Republic (1) within a European

integrated project CONffIDENCE (Contaminants in Food and

Feed: Inexpensive Detection for Control of Exposure; 2). This

method was studied within the presented collaborative study, for

which the analytes were narrowed down to include only PAHs

and some of the relevant PAH alkyl homologs (

see

Table 1 for the

list of 19 studied analytes and their abbreviations).

Table 1. PAHs included in the collaborative study

Name

Abbreviation

1,7-Dimethylphenanthrene

1,7-DMP

1-Methylnaphthalene

1-MN

1-Methylphenanthrene

1-MP

2,6-Dimethylnaphthalene

2,6-DMN

3-Methylchrysene

3-MC

Anthracene

Ant

Benz[

a

]anthracene

BaA

Benzo[

a

] pyrene

BaP

Benzo[

b

]fluoranthene

BbF

Benzo[

g,h,i

]perylene

BghiP

Benzo[

k

]fluoranthene

BkF

Chrysene

Chr

Dibenz[

a,h

]anthracene

DBahA

Fluoranthene

Flt

Fluorene

Fln

Indeno[1,2,3-

cd

]pyrene

IcdP

Naphthalene

Naph

Phenanthrene

Phe

Pyrene

Pyr

Table 2. PAH fortification levels (in µg/kg) in the shrimp, mussel, and oyster test samples

Shrimp

Mussel

Oyster

Low

Mid

High

Low

Mid

High

Low

Mid

High

PAH

Level 1

Level 2

Level 4

Level 1

Level 3

Level 4

Level 2

Level 3

Level 5

1,7-DMP

a

20

20

20

40

40

40

80

80

80

1-MN

20

75

200

20

100

200

75

100

250

1-MP

10

25

125

10

50

125

25

50

200

2,6-DMN

15

40

175

15

75

175

40

75

225

3-MC

10

30

145

10

90

145

30

90

225

Ant

5

10

40

5

15

40

10

15

60

BaA

5

15

60

5

25

60

15

25

100

BaP

2

5

25

2

10

25

5

10

50

BbF

5

10

75

5

30

75

10

30

100

BghiP

2

5

20

2

10

20

5

10

25

BkF

2

8

40

2

20

40

8

20

75

Chr

15

50

175

15

100

175

50

100

250

DBahA

2

5

15

2

10

15

5

10

20

Fln

5

15

50

5

25

50

15

25

75

Flt

10

25

100

10

50

100

25

50

150

IcdP

2

5

20

2

10

20

5

10

25

Naph

25

80

160

25

125

160

80

125

225

Phe

15

50

175

15

100

175

50

100

250

Pyr

15

40

125

15

75

125

40

75

200

a

 1,7-DMP served as a homogenization check, which was added to the blank mussel and oyster matrix during the homogenization step (prior to

fortification).

Candidates for 2016 Method of the Year

233