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© 2015 AOAC INTERNATIONAL

Table 2014.08I. PAH analytes and corresponding

13

C-PAHs

used for PAH signal normalization

Analyte

13

C-PAH used for signal normalization

Anthracene

Anthracene (

13

C

6

)

Benz[

a

]anthracene

Benz[

a

]anthracene (

13

C

6

)

Benzo[

a

]pyrene

Benzo[

a

]pyrene (

13

C

4

)

Benzo[

b

]fluoranthene

Benzo[

b

]fluoranthene (

13

C

6

)

Benzo[

g,h,i

]perylene

Benzo[

g,h,i

]perylene (

13

C

12

)

Benzo[

k

]fluoranthene

Benzo[

k

]fluoranthene (

13

C

6

)

Chrysene

Chrysene (

13

C

6

)

Dibenz[

a,h

]anthracene

Dibenz[

a,h

]anthracene (

13

C

6

)

Fluoranthene

Fluoranthene (

13

C

6

)

Fluorene

Fluorene (

13

C

6

)

Indeno[1,2,3-

cd

]pyrene

Indeno[1,2,3-

cd

]pyrene (

13

C

6

)

Naphthalene

Naphthalene (

13

C

6

)

Phenanthrene

Phenanthrene (

13

C

6

)

Pyrene

Pyrene (

13

C

6

)

1-Methylnaphthalene

Naphthalene (

13

C

6

)

2,6-Dimethylnaphthalene

Phenanthrene (

13

C

6

)

1-Methylphenanthrene

Phenanthrene (

13

C

6

)

1,7-Dimethylphenanthrene

Phenanthrene (

13

C

6

)

3-Methylchrysene

Chrysene (

13

C

6

)

where

c

13C-PAH

is the concentration of the corresponding

13

C-PAH in

the calibration standard solutions (in µg/L);

X

13C-PAH

is the amount

of the corresponding

13

C-PAH added to the sample (in ng); and

m

is the sample weight (in g). Based on the method procedure and

preparation of the calibration standard solutions,

c

13C-PAH

is 50 µg/L,

X

13C-PAH

is 50 ng, and

m

for the test samples is 10 g.

In the collaborative study, eight concentration levels were used

for the calibration, corresponding to 5, 10, 20, 50, 100, 200, 500,

and 1000 µg/L for benzo[

a

]pyrene and other lower-level PAHs, to

12.5, 25, 50, 125, 250, 500, 1250, and 2500 µg/L for higher-level

PAHs, except for naphthalene that was present at 25, 50, 100, 250,

500, 1000, 2500, and 5000 µg/L. Coefficients of determination (r

2

)

should be 0.990 or greater and back-calculated concentrations of

the calibration standards should not exceed ±20% of theoretical. For

lower concentration levels, a limited calibration curve (without the

higher-end concentration points) may be used for better accuracy.

If a well-characterized quadratic relationship occurs, then a best-

fitted quadratic curve may be used for calibration. Otherwise, if

the back-calculated concentrations exceed ±20% of theoretical,

normalized signals of the nearest two calibration standards that

enclose the analyte signal in the sample can be used to interpolate

the analyte concentration in the final extract.

References: (1) Kalachova, K., Pulkrabova, J., Drabova, L.,

Cajka, T., Kocourek, V., & Hajslova, J. (2011)

Anal. Chim. Acta

707

, 84–91.

http://dx.doi

.

org/10.1016/j.aca.2011.09.016

J. AOAC Int . 98 , 477 (2105)

DOI: 10.5740/jaoacint.15-032

Posted: April 30, 2015

Candidates for 2016 Method of the Year

231