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J

ulshamn

et al

.:

J

ournal of

AOAC I

nternational

V

ol

.

96, N

o

. 5, 2013 

1101

Determination of Arsenic, Cadmium, Mercury, and Lead in

Foods by Pressure Digestion and Inductively Coupled Plasma/

Mass Spectrometry: First Action 2013.06

K

aare

J

ulshamn

and

A

mund

M

aage

National Institute of Nutrition and Seafood Research (NIFES), PO Box 2029 Nordnes, N-5817 Bergen, Norway

H

ilde

S

kaar

N

orli

National Veterinary Institute, Department of Food and Feed Hygiene, Nordic Committee on Food Analysis, PO Box 8156, Dep.,

N-0033 Oslo, Norway

K

arl

H. G

robecker

European Commission Joint Research Centre, Institute for Reference Materials and Measurements (IRMM), B-2440 Geel, Belgium

L

ars

J

orhem

National Food Administration, Box 622, SE-751 26 Uppsala, Sweden

P

eter

F

echer

Bayerisches Landesamt für Gesundheit und Lebensmittelsicherheit, Zentrallabor Chemie, Sachgebiet N6, Eggenreuther Weg 43

D-91058 Erlangen, Germany

D

awn

D

owell

AOAC INTERNATIONAL, 481 North Frederick Ave, Suite 500, Gaithersburg, MD 20877-2417

Submitted for publication April 22, 2013.

The method was approved by the Method-Centric Committee for

Elemental Contaminants in Food as First Action.

The AOAC Method-Centric Committee for Elemental

Contaminants in Food invites method users to provide feedback on the

First Action methods. Feedback from method users will help verify

that the methods are fit for purpose and are critical to gaining global

recognition and acceptance of the methods. Comments can be sent

directly to the corresponding author or

methodfeedback@aoac.org.

Corresponding author’s e-mail:

kju@nifes.no

DOI: 10.5740/jaoacint.13-143

RESIDUES AND TRACE ELEMENTS

The method for the determination of As, Cd, Hg, and

Pb in foods by pressure digestion and inductively

coupled plasma (ICP)/MS, previously published in

J. AOAC Int.

90, 844–856 (2007), was approved as

First Action 2013.06 on April 9, 2013 by the Method-

Centric Committee for Elemental Contaminants in

Food. Digestion occurs using nitric acid in a closed

vessel with elevated temperature and pressure

by conventional or microwave-assisted heating.

Determination occurs using ICP/MS. The elemental

concentration ranges for As were 0.06–21.4, for

Cd 0.03–28.3, for Hg 0.04–0.6, and for Pb 0.01–2.4

in mg/kg dry matter. The repeatability RSD (RSD

r

)

ranged from 3.8 to 24% for As, 2.6 to 6.9% for Cd, 4.8

to 8.3% for Hg, and 2.9 to 27% for Pb. Reproducibility

RSD (RSD

R

) ranged from 9.0 to 28% for As, 2.8 to

18% for Cd, 9.9 to 24% for Hg, and 8 to 50% for Pb.

H

eavy metal poisoning from elements like As, Cd, Hg,

and Pb has become a concern for most industrialized

countries (1). These toxic metals have a negative effect

on physiological processes. Because of the negative health

effects, governments have begun to implement regulations on

the levels of contaminants allowed in the food supply to protect

the public. The implementation of these regulations raises a

need to have validated analytical methods that produce reliable

and accurate results to ensure compliance. The method has been

reviewed and found acceptable for the determination of As, Cd,

Hg, and Pb in a variety of foods.

AOAC Official Method 2013.06

Arsenic, Cadmium, Mercury, and Lead in Foods

Pressure Digestion and Inductively Coupled Plasma/

Mass Spectrometry

First Action 2013

(Applicable to the determination of As, Cd, Hg, and Pb in a

variety of foods by pressure digestion and ICP/MS. Method is

capable of determining As, Cd, Pb, and Hg at or above 0.06,

0.03, 0.04, and 0.09 mg/kg dry matter, respectively.) For the

complete method,

see

the publication in

J. AOAC Int.

(2).

Results

The results of the collaborative study (Table 1; 2) show this

method to be suitable for the determination of As, Cd, Hg, and

Pb in a variety of foods. The elemental concentration ranges for

As were 0.06–21.4, for Cd 0.03–28.3, for Hg 0.04–0.6, and for

Pb 0.01–2.4 in mg/kg dry matter. The repeatability RSD (RSD

r

)

ranged from 3.8 to 24% for As, 2.6 to 6.9% for Cd, 4.8 to 8.3%

for Hg, and 2.9 to 27% for Pb. Reproducibility RSD (RSD

R

)

ranged from 9.0 to 28% for As, 2.8 to 18% for Cd, 9.9 to 24%

for Hg, and 8 to 50% for Pb.

References

 (1) Sinicropi, M.S., Amantea, D., Caruso, A., & Saturnino, C.

(2010)

Arch. Toxicol.

84

, 501–520.

http://dx.doi.org/10.1007/

s00204-010-0544-6

 (2) Julshamn, K., Maage, A., Norli, H., Grobecker, K., Jorhem, L.,

& Fecher, P. (2007)

J. AOAC Int.

90

,

844–856

93