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Atomic Absorption
Authors
Praveen Sarojam, Ph.D.
Jianmin Chen, Ph.D.
PerkinElmer, Inc.
Shelton, CT 06484 USA

Analysis of Arsenic,
Cadmium and Lead
in Chinese Spice Mixtures
using Graphite Furnace
Atomic Absorption
Spectrophotometry

Introduction

Spices are dried parts of plants.
Together with herbs, these plants
grow widely in various regions of the
world and have been used for several
purposes since ancient times. Most
are fragrant, aromatic and pungent
and are used for culinary purposes
to improve color, aroma, palatability
and acceptability of food.1 In addition,
they are also used in folk medicine
as antiscorbutic, antispasmodic, tonic,
carminative agents against bronchitis,
ulcers and as diuretics, depuratives and vermifuges. Also, some species are used as teaflavoring agents in several regions. Natural food spices, such as pepper and mustard, have
been reported to contain significant quantities of some heavy metals, including cadmium,
lead and arsenic. Exposure to trace and heavy metals above the permissible affects human
health and may result in illness to human fetus, abortion and preterm labor, as well as
mental retardation to children. Adults also may experience high blood pressure, fatigue
and kidney and neurological disorders.1 Contamination with heavy metals may be accidental
(e.g. contamination of environment during plant cultivation) or deliberate – in some cultures, according to traditional belief, specially treated heavy metals are associated with
health benefits and are thus an intentional ingredient of traditional remedies. Spices and
herbal plants may contain heavy-metal ions over a wide range of concentrations.2,3
India and China have a high diversity of plants used as spices,
herbs, and traditional medicines. Several herbs and spices
are either produced on small farmlands or naturally grow
in different regions. There is often little information available
about the safety of those plants and their products in
respect to heavy metal contamination. Due to the significant
amount of spices consumed, it is important to know the
toxic metal contents in these spices.4
The objective of this work is two-fold: (1) to accurately
analyze the levels of toxic heavy metals like lead, cadmium
and arsenic that may be present in some major spice brands
available in the local markets in China, by using graphite
furnace atomic absorption spectrophotometry (GFAAS); (2)
to cross-reference these measured levels to the recommended
limits specified by the U.S. FDA.

A Multiwave™ 3000 Microwave Sample Preparation System
(PerkinElmer/Anton-Paar) was used for the microwaveassisted digestion (Figure 2). This is an industrial-type microwave oven which is equipped with various accessories to
optimize the sample digestion. The samples were digested
in the 8XF100 rotor using eight 100 mL high-pressure vessels
made of PTFE-TFM protected with its individual ceramic
jackets. TFM is chemically modified PTFE that has enhanced
mechanical properties at high temperatures compared to
the conventional PTFE. This vessel has a working pressure
of 60 bars (870 psi) and temperatures of up to 260 ˚C.

Experimental
The measurements were performed using a PerkinElmer®
AAnalyst™ 800 Atomic Absorption Spectrophotometer
(Shelton, CT, USA) equipped with the intuitive WinLab32™
for AA (Version 6.5) software, which features all the tools
to analyze samples, report and archive data and ensure
regulatory compliance. The high-efficiency optical system
and solid-state detector used in this spectrophotometer
provide outstanding signal-to-noise ratios. This solid-state
detector is also highly efficient at low UV and high wavelengths at one time. It also features longitudinal Zeemaneffect background correction for graphite furnace analysis.
The use of a transversely heated graphite atomizer (THGA)
provides uniform temperature distribution across the entire
length of the graphite tube. This eliminates the memory
effect inherent with high-matrix sample analysis. The THGA
features an integrated L’vov platform which is useful in
overcoming potential chemical interference effects common
to the GFAAS technique. High-energy electrodeless discharge
lamps (EDLs) were used for all the elements.

Figure 1. PerkinElmer AAnalyst 800 Atomic Absorption Spectrophotometer.

2

Figure 2. PerkinElmer/Anton-Paar Multiwave 3000 Microwave Sample
Preparation System.

Standards, Chemicals and Certified Reference Materials
PerkinElmer single-element calibration standards for Atomic
Spectroscopy were used as the stock standards for preparing
the working standards. Working standards were prepared
by serial volume/volume dilution in polypropylene vials
(Sarstedt®, Germany)
ASTM® Type I water (from a Millipore® filtration system –
Millipore® Corporation, Billerica, Massachusetts, USA)
acidified with 0.2% Suprapur® nitric acid, from Merck®
(Darmstadt, Germany) was used as the calibration blank and
for all dilutions. Chemical modifiers were prepared from
stock solutions, by diluting with acidified Millipore® water
and were added automatically to each standard, blank and
sample by the AS-800 autosampler, an integral part of the
AAnalyst 800. Micropipettes (Eppendorf®, Germany) with
disposable tips were used for pippetting solutions.
NIST® 1573e certified reference material for trace metals in
tomato leaves, GBW 10016 certified reference material for
trace metals in tea leaves, and GBW 09101 certified reference material for trace metals in human hair were used to
validate the method developed. Multi-element ICP standards
for trace-metal ions in nitric acid (Spex. Certiprep.®, New
Jersey, USA), prepared at concentrations of the midpoint of
the calibration curves for different elements, were used as
quality control (QC) check standards.
Sample and Certified Reference Material Preparation
Four branded powdered spice and herb samples available in
China (five-spice mix, ground szechuan, five-spice powder
and curry powder), bought from a local Chinese supermarket,
were used for the analysis.
Approx. 0.5 g of each sample, accurately weighed in duplicate, was transferred to the digestion vessels of the microwave digestion system and the sample digestion was done
in accordance with the program given in Table 3 (Page 4).
The digested samples were diluted with 0.2% HNO3 and made
up to 20 mL in polypropylene vials. The certified reference
materials were also digested in a similar manner.
Plastic bottles were cleaned by soaking with 10% volume/
volume HNO3 for at least 24 hours and rinsed abundantly
in de-ionized water before use. The instrumental conditions
for furnace experiments are given in Table 1, and the graphite
furnace temperature programs are listed in Appendix I (Page 6).
Heated injection at 90 ˚C was used for all the furnace experiments. Pyrolytically-coated graphite tubes with integrated
platforms were used. The autosampler cups were soaked in
20% nitric acid overnight to minimize sample contamination,
and thoroughly rinsed with 0.5% HNO3 acid before use.
Five-point calibration curves (four standards and one blank)
were constructed for all the metal ions and the calibrationcurve correlation coefficient was ensured to be better than
0.999 before the start of the sample analysis.

Table 1. Optimized experimental conditions of AAnalyst 800.
Element	

Cd	

Pb	

As

Wavelength (nm)	 228.8	

283.3	

193.7

Slit (nm)	

0.7	

0.7	

0.7

Mode	

AA-BG	

AA-BG	

AA-BG

Calibration	
	
	

Linear with	
calculated 	
intercept	

Linear with	
calculated	
intercept	

Linear with
calculated
intercept

Lamp	

EDL	

EDL	

EDL

Current (mA)	

230	

440	

380

Standards (µg/L)	 0.2, 0.5, 1.0	

5.0, 10, 25	

5.0, 10, 25

Correlation	
Coefficient	

0.9991	

0.9992

Read Time (sec)	 5	

5	

Peak Area	

Peak Area	

90	

90	

20	

20	

0.05 mg 	
NH 4H2PO4 	
and 0.003 mg 	
Mg(NO3)2	
5	

5	

1	

1200	

15	

15	

1

2	

0		

15	

3

Weight Taken	 ~500 mg	

HNO3	

5.0 mL

H 2O 2	

1.0 mL	

Rate	

0.5 bar/sec

Pressure	

55 Bars		

Results and Discussions
The validity of the developed method has been ensured by
incorporating various quality control (QC) checks and analysis
of certified reference materials (CRMs). The agreement
between the certified values and the measured values were
excellent, which demonstrates the accuracy of the generated calibration as well as the overall accuracy of the developed method (Table 3 – Page 4). The slightly higher values
obtained for Cd in NIST® CRM 1573e is due to the fact that
the container of the CRM was opened a few years ago and
the reference material was left in a polyethylene bag where
contamination for Cd had occurred. This was confirmed
by analyzing the same CRM using an ICP-MS (PerkinElmer
ELAN® DRC-e) where a value of 2.37 µg/g was obtained. The
QC standard gave excellent recovery with a variation of less
than 10% usually prescribed by the regulatory bodies (Table
4 – Page 4). There was virtually no difference between the
QC standard which was performed immediately after calibration and the QC standard which was analyzed at the end of
the analysis with a time difference of more than three hours.
This shows the long-term stability of the instrument. Method
detection limits (MDLs) were calculated (Table 5 – Page 4)
based on the standard deviation of seven replicates of the
reagent blanks (student t-value of 3.14 for a confidence
interval of 98%). These limits were obtained under routine
operating conditions, and this is not reflective of the optimum
detection limits achievable by the system. The extremely lower
detection limits obtained show the capability of the AAnalyst
800 spectrometer in analyzing difficult matrices at the
measured concentrations.

0.05 mg	
0.005 mg Pd
NH4H2PO4	
and 0.003 mg
and 0.003 mg	 Mg(NO3)2
Mg(NO3)2	

Modifier	
Volume (µL)	

Fan

20

Matrix Modifier	
	
	
	

Hold Time	
(min)	

90

Sample 	
Volume (µL)	

Ramp Time	
(min)	

Peak Area

Injection	
Temp (˚C)	

Sequence	
Power	
		

5

Measurement	

Table 2. Program used for the digestion of spices and herbs
with the Multiwave.

0.9997	

5
3
Table 3. Analysis of certified reference materials.
Analyte	

NIST® 1573e	

GBW 09101	

GBW 10016

	
	

Certified	
Value (µg/g)	

Measured 	
Value (µg/g)	

Certified	
Value (µg/g)	

Measured	
Value (µg/g)	

Certified	
Value (µg/g)	

Measured
Value (µg/g)

Pb	

*	

–	

3.83 ± 0.18	

3.83 ± 0.54	

1.5 ± 0.2	

1.3 ± 0.5

Cd	

1.52	

2.24	

0.072 ± 0.010	

0.075 ± 0.01	

0.062 ± 0.01	

0.06 ± 0.02

As	

0.112	

0.15	

0.198 ± 0.023	

0.23 ± 0.03	

0.09 ± 0.01	

0.07 ± 0.02

*Not a reference element

Table 4. Results of QC recovery studies.
Analyte	
	
	
	

Prepared 	
Concentration	
(µg/L) QC	

Measured	
% QC	
Concentration 	
Recovery	
(µg/L) QC		
(analyzed at 10:00 am)		

(analyzed at 10:00 am)	

Prepared	
Concentration	
(µg/L) QC	

(analyzed at 1:30 pm)	

Measured	
Concentration	
(µg/L) QC	

% QC
Recovery

(analyzed at 1:30 pm)

Pb	

12.5	

12.6	

101	

12.5	

12.6	

101

Cd	

0.50	

0.50	

100	

0.50	

0.50	

100

As	

12.5	

12.1	

97	

12.5	

13.3	

106

Table 5. Method detection limits (MDLs).
Analyte	

MDL (µg/kg)

Pb	

9

Cd	

2

As	

6

Table 6. Analysis of spices and herbs samples using GFAAS.
Analyte	
(µg/g)	

Five-Spice	
Mix	

Ground 	
Szechuan	

Five-Spice 	
Powder	

Five-Spice 	
Powder Duplicate	

Curry	
Powder	

Curry
Powder Duplicate

Pb	

2.42	

4.48	

6.30	

6.93	

1.21	

1.22

Cd	

0.25	

0.07	

0.25	

0.23	

0.38	

0.35

As	

0.12	

0.07	

0.16	

0.15	

0.14	

0.14

Table 7. Analysis of spices and herbs samples using ICP-MS.*
Analyte(µg/g)	

Five-Spice Mix	

Ground Szechuan 	

Five-Spice Powder	

Curry Powder

Pb	

2.72	

4.69	

6.04	

1.28

Cd	

0.11	

0.06	

0.27	

0.26

As	

0.19	

0.16	

0.18	

0.31

*Different set of similar samples

4
Conclusions
An accurate and reliable microwave-assisted sample
pretreatment procedure for the determination of arsenic,
cadmium and lead in spices using GFAAS is described.
The spices contain a number of organic substances of
different stability and impurities of sparingly soluble mineral
components. Incomplete mineralization of samples during
the microwave-digestion process may cause difficulty in
transferring analytes into solution and this also disturbs
spectrochemical measurements.5 Application of concentrated
HNO3 along with hydrogen peroxide for mineralization of
spices and herbs leads to the complete digestion of samples,
which is proven by determined values of the analytes in
various CRMs. Toxicity of medicinal spices and herbs is of
much greater concern today than ever before. In recent

years, much emphasis is being laid on toxic-element
contents, as several European Union countries have banned
many varieties of ayurvedic drugs. The results in Table 6 and
7 (Page 4) show that the levels of arsenic, cadmium and lead
in all the samples analyzed were well within the permissible
limits of 10, 0.3 and 10 mg/kg respectively, as specified by
the U.S. FDA. The results confirmed that the determination
of arsenic, cadmium and lead after acid solubilization of
spice-mixture samples by microwave digestion can be
performed by GFAAS without any interference and the
same has been cross-checked by analyzing a different set
of similar samples with ICP-MS analysis (using a PerkinElmer
ELAN DRC-e ICP-MS). The good agreement of the values
obtained with standard ICP-MS and GFAAS analysis further
confirmed the accuracy of the method developed.

References
1.	H. Mubeen, I. Naeem, A. Taskeen and Z. Saddiqe, New York Science Journal, 2 (5) (2009) 1554-0200.
2.	K.K. Gupta, S. Bhattacharjee, S. Kar, S. Chakrabarty, P. Thakar, G. Bhattacharyya and S.C. Srivastava, Comm. Soil Plant
Anal., 34 (2003) 681-693.
3.	T.M. Ansari, N. Ikram, M. Najam-ul-Haq, O. Fayyaz, I. Ghafoor and N. Khalid, J. Biol. Sci., 4 (2004) 95-99.
4.	R.P. Choudhury and A.N. Garg, Food Chemistry, 104 (2007) 1454-1463.
5.	I. Baranowska, K. Srogi, A. Włochowicz, K. Szczepanik, Polish Journal of Environmental Studies, 11( 5) (2002) 467-471.

5
Appendix I. Graphite Furnace Temperature Program.
Element	 Step	 Temp ˚C	
			

Ramp Time	
(sec)	

Hold Time	
(sec)	

Internal Gas	
Flow (mL/min)	

Gas Type

Cd	
	
	
	
	

1	
2	
3	
4	
5	

110	
130	
500	
1500	
2450	

1	
15	
10	
0	
1	

30	
30	
20	
5	
3	

250	
250	
250	
0	
250	

Argon
Argon
Argon
Argon
Argon

As	
	
	
	
	

1	
2	
3	
4	
5	

110	
130	
1200	
2000	
2450	

1	
15	
10	
0	
1	

30	
30	
20	
5	
3	

250	
250	
250	
0	
250	

Argon
Argon
Argon
Argon
Argon

Pb	
	
	
	
	

1	
2	
3	
4	
5	

110	
130	
850	
1600	
2450	

1	
15	
10	
0	
1	

30	
30	
20	
5	
3	

250	
250	
250	
0	
250	

Argon
Argon
Argon
Argon
Argon

Appendix II. Calibration Graphs for Different Analytes.

Appendix III. Atomization Profiles of Lower Standard and Some Samples.

PerkinElmer, Inc.
940 Winter Street
Waltham, MA 02451 USA	
P: (800) 762-4000 or
(+1) 203-925-4602
www.perkinelmer.com

For a complete listing of our global offices, visit www.perkinelmer.com/ContactUs
Copyright ©2010, PerkinElmer, Inc. All rights reserved. PerkinElmer® is a registered trademark of PerkinElmer, Inc. All other trademarks are the property of their respective owners.
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Analysis of Arsenic, Cadmium and Lead in Chinese Spice Mixtures using Graphite Furnace Atomic Absorption Spectrophotometry

  • 1. a p p l i c at i o n N o t e Atomic Absorption Authors Praveen Sarojam, Ph.D. Jianmin Chen, Ph.D. PerkinElmer, Inc. Shelton, CT 06484 USA Analysis of Arsenic, Cadmium and Lead in Chinese Spice Mixtures using Graphite Furnace Atomic Absorption Spectrophotometry Introduction Spices are dried parts of plants. Together with herbs, these plants grow widely in various regions of the world and have been used for several purposes since ancient times. Most are fragrant, aromatic and pungent and are used for culinary purposes to improve color, aroma, palatability and acceptability of food.1 In addition, they are also used in folk medicine as antiscorbutic, antispasmodic, tonic, carminative agents against bronchitis, ulcers and as diuretics, depuratives and vermifuges. Also, some species are used as teaflavoring agents in several regions. Natural food spices, such as pepper and mustard, have been reported to contain significant quantities of some heavy metals, including cadmium, lead and arsenic. Exposure to trace and heavy metals above the permissible affects human health and may result in illness to human fetus, abortion and preterm labor, as well as mental retardation to children. Adults also may experience high blood pressure, fatigue and kidney and neurological disorders.1 Contamination with heavy metals may be accidental (e.g. contamination of environment during plant cultivation) or deliberate – in some cultures, according to traditional belief, specially treated heavy metals are associated with health benefits and are thus an intentional ingredient of traditional remedies. Spices and herbal plants may contain heavy-metal ions over a wide range of concentrations.2,3
  • 2. India and China have a high diversity of plants used as spices, herbs, and traditional medicines. Several herbs and spices are either produced on small farmlands or naturally grow in different regions. There is often little information available about the safety of those plants and their products in respect to heavy metal contamination. Due to the significant amount of spices consumed, it is important to know the toxic metal contents in these spices.4 The objective of this work is two-fold: (1) to accurately analyze the levels of toxic heavy metals like lead, cadmium and arsenic that may be present in some major spice brands available in the local markets in China, by using graphite furnace atomic absorption spectrophotometry (GFAAS); (2) to cross-reference these measured levels to the recommended limits specified by the U.S. FDA. A Multiwave™ 3000 Microwave Sample Preparation System (PerkinElmer/Anton-Paar) was used for the microwaveassisted digestion (Figure 2). This is an industrial-type microwave oven which is equipped with various accessories to optimize the sample digestion. The samples were digested in the 8XF100 rotor using eight 100 mL high-pressure vessels made of PTFE-TFM protected with its individual ceramic jackets. TFM is chemically modified PTFE that has enhanced mechanical properties at high temperatures compared to the conventional PTFE. This vessel has a working pressure of 60 bars (870 psi) and temperatures of up to 260 ˚C. Experimental The measurements were performed using a PerkinElmer® AAnalyst™ 800 Atomic Absorption Spectrophotometer (Shelton, CT, USA) equipped with the intuitive WinLab32™ for AA (Version 6.5) software, which features all the tools to analyze samples, report and archive data and ensure regulatory compliance. The high-efficiency optical system and solid-state detector used in this spectrophotometer provide outstanding signal-to-noise ratios. This solid-state detector is also highly efficient at low UV and high wavelengths at one time. It also features longitudinal Zeemaneffect background correction for graphite furnace analysis. The use of a transversely heated graphite atomizer (THGA) provides uniform temperature distribution across the entire length of the graphite tube. This eliminates the memory effect inherent with high-matrix sample analysis. The THGA features an integrated L’vov platform which is useful in overcoming potential chemical interference effects common to the GFAAS technique. High-energy electrodeless discharge lamps (EDLs) were used for all the elements. Figure 1. PerkinElmer AAnalyst 800 Atomic Absorption Spectrophotometer. 2 Figure 2. PerkinElmer/Anton-Paar Multiwave 3000 Microwave Sample Preparation System. Standards, Chemicals and Certified Reference Materials PerkinElmer single-element calibration standards for Atomic Spectroscopy were used as the stock standards for preparing the working standards. Working standards were prepared by serial volume/volume dilution in polypropylene vials (Sarstedt®, Germany) ASTM® Type I water (from a Millipore® filtration system – Millipore® Corporation, Billerica, Massachusetts, USA) acidified with 0.2% Suprapur® nitric acid, from Merck® (Darmstadt, Germany) was used as the calibration blank and for all dilutions. Chemical modifiers were prepared from stock solutions, by diluting with acidified Millipore® water and were added automatically to each standard, blank and sample by the AS-800 autosampler, an integral part of the AAnalyst 800. Micropipettes (Eppendorf®, Germany) with disposable tips were used for pippetting solutions. NIST® 1573e certified reference material for trace metals in tomato leaves, GBW 10016 certified reference material for trace metals in tea leaves, and GBW 09101 certified reference material for trace metals in human hair were used to validate the method developed. Multi-element ICP standards for trace-metal ions in nitric acid (Spex. Certiprep.®, New Jersey, USA), prepared at concentrations of the midpoint of the calibration curves for different elements, were used as quality control (QC) check standards.
  • 3. Sample and Certified Reference Material Preparation Four branded powdered spice and herb samples available in China (five-spice mix, ground szechuan, five-spice powder and curry powder), bought from a local Chinese supermarket, were used for the analysis. Approx. 0.5 g of each sample, accurately weighed in duplicate, was transferred to the digestion vessels of the microwave digestion system and the sample digestion was done in accordance with the program given in Table 3 (Page 4). The digested samples were diluted with 0.2% HNO3 and made up to 20 mL in polypropylene vials. The certified reference materials were also digested in a similar manner. Plastic bottles were cleaned by soaking with 10% volume/ volume HNO3 for at least 24 hours and rinsed abundantly in de-ionized water before use. The instrumental conditions for furnace experiments are given in Table 1, and the graphite furnace temperature programs are listed in Appendix I (Page 6). Heated injection at 90 ˚C was used for all the furnace experiments. Pyrolytically-coated graphite tubes with integrated platforms were used. The autosampler cups were soaked in 20% nitric acid overnight to minimize sample contamination, and thoroughly rinsed with 0.5% HNO3 acid before use. Five-point calibration curves (four standards and one blank) were constructed for all the metal ions and the calibrationcurve correlation coefficient was ensured to be better than 0.999 before the start of the sample analysis. Table 1. Optimized experimental conditions of AAnalyst 800. Element Cd Pb As Wavelength (nm) 228.8 283.3 193.7 Slit (nm) 0.7 0.7 0.7 Mode AA-BG AA-BG AA-BG Calibration Linear with calculated intercept Linear with calculated intercept Linear with calculated intercept Lamp EDL EDL EDL Current (mA) 230 440 380 Standards (µg/L) 0.2, 0.5, 1.0 5.0, 10, 25 5.0, 10, 25 Correlation Coefficient 0.9991 0.9992 Read Time (sec) 5 5 Peak Area Peak Area 90 90 20 20 0.05 mg NH 4H2PO4 and 0.003 mg Mg(NO3)2 5 5 1 1200 15 15 1 2 0 15 3 Weight Taken ~500 mg HNO3 5.0 mL H 2O 2 1.0 mL Rate 0.5 bar/sec Pressure 55 Bars Results and Discussions The validity of the developed method has been ensured by incorporating various quality control (QC) checks and analysis of certified reference materials (CRMs). The agreement between the certified values and the measured values were excellent, which demonstrates the accuracy of the generated calibration as well as the overall accuracy of the developed method (Table 3 – Page 4). The slightly higher values obtained for Cd in NIST® CRM 1573e is due to the fact that the container of the CRM was opened a few years ago and the reference material was left in a polyethylene bag where contamination for Cd had occurred. This was confirmed by analyzing the same CRM using an ICP-MS (PerkinElmer ELAN® DRC-e) where a value of 2.37 µg/g was obtained. The QC standard gave excellent recovery with a variation of less than 10% usually prescribed by the regulatory bodies (Table 4 – Page 4). There was virtually no difference between the QC standard which was performed immediately after calibration and the QC standard which was analyzed at the end of the analysis with a time difference of more than three hours. This shows the long-term stability of the instrument. Method detection limits (MDLs) were calculated (Table 5 – Page 4) based on the standard deviation of seven replicates of the reagent blanks (student t-value of 3.14 for a confidence interval of 98%). These limits were obtained under routine operating conditions, and this is not reflective of the optimum detection limits achievable by the system. The extremely lower detection limits obtained show the capability of the AAnalyst 800 spectrometer in analyzing difficult matrices at the measured concentrations. 0.05 mg 0.005 mg Pd NH4H2PO4 and 0.003 mg and 0.003 mg Mg(NO3)2 Mg(NO3)2 Modifier Volume (µL) Fan 20 Matrix Modifier Hold Time (min) 90 Sample Volume (µL) Ramp Time (min) Peak Area Injection Temp (˚C) Sequence Power 5 Measurement Table 2. Program used for the digestion of spices and herbs with the Multiwave. 0.9997 5 3
  • 4. Table 3. Analysis of certified reference materials. Analyte NIST® 1573e GBW 09101 GBW 10016 Certified Value (µg/g) Measured Value (µg/g) Certified Value (µg/g) Measured Value (µg/g) Certified Value (µg/g) Measured Value (µg/g) Pb * – 3.83 ± 0.18 3.83 ± 0.54 1.5 ± 0.2 1.3 ± 0.5 Cd 1.52 2.24 0.072 ± 0.010 0.075 ± 0.01 0.062 ± 0.01 0.06 ± 0.02 As 0.112 0.15 0.198 ± 0.023 0.23 ± 0.03 0.09 ± 0.01 0.07 ± 0.02 *Not a reference element Table 4. Results of QC recovery studies. Analyte Prepared Concentration (µg/L) QC Measured % QC Concentration Recovery (µg/L) QC (analyzed at 10:00 am) (analyzed at 10:00 am) Prepared Concentration (µg/L) QC (analyzed at 1:30 pm) Measured Concentration (µg/L) QC % QC Recovery (analyzed at 1:30 pm) Pb 12.5 12.6 101 12.5 12.6 101 Cd 0.50 0.50 100 0.50 0.50 100 As 12.5 12.1 97 12.5 13.3 106 Table 5. Method detection limits (MDLs). Analyte MDL (µg/kg) Pb 9 Cd 2 As 6 Table 6. Analysis of spices and herbs samples using GFAAS. Analyte (µg/g) Five-Spice Mix Ground Szechuan Five-Spice Powder Five-Spice Powder Duplicate Curry Powder Curry Powder Duplicate Pb 2.42 4.48 6.30 6.93 1.21 1.22 Cd 0.25 0.07 0.25 0.23 0.38 0.35 As 0.12 0.07 0.16 0.15 0.14 0.14 Table 7. Analysis of spices and herbs samples using ICP-MS.* Analyte(µg/g) Five-Spice Mix Ground Szechuan Five-Spice Powder Curry Powder Pb 2.72 4.69 6.04 1.28 Cd 0.11 0.06 0.27 0.26 As 0.19 0.16 0.18 0.31 *Different set of similar samples 4
  • 5. Conclusions An accurate and reliable microwave-assisted sample pretreatment procedure for the determination of arsenic, cadmium and lead in spices using GFAAS is described. The spices contain a number of organic substances of different stability and impurities of sparingly soluble mineral components. Incomplete mineralization of samples during the microwave-digestion process may cause difficulty in transferring analytes into solution and this also disturbs spectrochemical measurements.5 Application of concentrated HNO3 along with hydrogen peroxide for mineralization of spices and herbs leads to the complete digestion of samples, which is proven by determined values of the analytes in various CRMs. Toxicity of medicinal spices and herbs is of much greater concern today than ever before. In recent years, much emphasis is being laid on toxic-element contents, as several European Union countries have banned many varieties of ayurvedic drugs. The results in Table 6 and 7 (Page 4) show that the levels of arsenic, cadmium and lead in all the samples analyzed were well within the permissible limits of 10, 0.3 and 10 mg/kg respectively, as specified by the U.S. FDA. The results confirmed that the determination of arsenic, cadmium and lead after acid solubilization of spice-mixture samples by microwave digestion can be performed by GFAAS without any interference and the same has been cross-checked by analyzing a different set of similar samples with ICP-MS analysis (using a PerkinElmer ELAN DRC-e ICP-MS). The good agreement of the values obtained with standard ICP-MS and GFAAS analysis further confirmed the accuracy of the method developed. References 1. H. Mubeen, I. Naeem, A. Taskeen and Z. Saddiqe, New York Science Journal, 2 (5) (2009) 1554-0200. 2. K.K. Gupta, S. Bhattacharjee, S. Kar, S. Chakrabarty, P. Thakar, G. Bhattacharyya and S.C. Srivastava, Comm. Soil Plant Anal., 34 (2003) 681-693. 3. T.M. Ansari, N. Ikram, M. Najam-ul-Haq, O. Fayyaz, I. Ghafoor and N. Khalid, J. Biol. Sci., 4 (2004) 95-99. 4. R.P. Choudhury and A.N. Garg, Food Chemistry, 104 (2007) 1454-1463. 5. I. Baranowska, K. Srogi, A. Włochowicz, K. Szczepanik, Polish Journal of Environmental Studies, 11( 5) (2002) 467-471. 5
  • 6. Appendix I. Graphite Furnace Temperature Program. Element Step Temp ˚C Ramp Time (sec) Hold Time (sec) Internal Gas Flow (mL/min) Gas Type Cd 1 2 3 4 5 110 130 500 1500 2450 1 15 10 0 1 30 30 20 5 3 250 250 250 0 250 Argon Argon Argon Argon Argon As 1 2 3 4 5 110 130 1200 2000 2450 1 15 10 0 1 30 30 20 5 3 250 250 250 0 250 Argon Argon Argon Argon Argon Pb 1 2 3 4 5 110 130 850 1600 2450 1 15 10 0 1 30 30 20 5 3 250 250 250 0 250 Argon Argon Argon Argon Argon Appendix II. Calibration Graphs for Different Analytes. Appendix III. Atomization Profiles of Lower Standard and Some Samples. PerkinElmer, Inc. 940 Winter Street Waltham, MA 02451 USA P: (800) 762-4000 or (+1) 203-925-4602 www.perkinelmer.com For a complete listing of our global offices, visit www.perkinelmer.com/ContactUs Copyright ©2010, PerkinElmer, Inc. All rights reserved. PerkinElmer® is a registered trademark of PerkinElmer, Inc. All other trademarks are the property of their respective owners. 009271_01