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Analysis of “The Big Four” Heavy
Metals in Hops by Graphite Furnace
Atomic Absorption and Cold Vapor
Mercury
Robert H. Clifford, Dan Davis, Keith Long, and Justin Masone,
Shimadzu Scientific Instruments, Columbia, MD, USA
Introduction
Plants concentrate metals by absorbing them from the soil in which they are grown.
Some metals are beneficial and essential for life whereas other metals are highly toxic
and have negative effects with even the lowest of levels. Because of their toxicity,
quantification of these elements is needed. This application will investigate the
preparation and analysis for heavy metals in Cascade Hops using Shimadzu AA-7000
with Graphite Furnace Atomic Absorption and Cold Vapor techniques. Spike and
Recovery tests are performed at or below the analysis target levels to ensure accuracy
and sensitivity of the technique.
Element
Analysis
Target PPM
As Prepped
(50x dil.)
PPB
Lead 1.20 24
Cadmium 0.82 16
Mercury 0.40 8.0
Arsenic 2.00 40 Table 1. Metals Target Analysis
Cascade Hops were purchased pre-dried and ground. 0.5 grams of Hops were
added to a closed vessel digester, and 4 mL of Nitric Acid, 2 mL of 30% H2O2,
and 1 mL of DI H2O were added. The sample was ramped to 900 watts over
15 minutes and held for another 20 minutes at that power. The sample was
then allowed to cool and brought to 25 mL total volume with DI H2O.
2 mL of the solution was reserved for analysis of Cd, As and Pb by Graphite
Furnace Atomic Absorption. 20 mL of sample was reserved for Hg analysis by
Cold Vapor; 10 mL of untreated sample, and 10 mL of sample spiked to 1 ppb
Hg.
Experiment: Sample Preparation
Fig. 1: Digestion/Preparation Procedure
Shimadzu AA-700
Experiment: Sample Preparation
Experiment: Analytical Method and
Conditions
Measurement was conducted using the calibration curve method. The main
measurement parameters of the instrument are shown in Table 2. The standard
solutions were prepared by diluting commercially available standard solutions for
atomic absorption measurement. 100 mL of calibration solution was prepared at 20
ppb As, Pb, 10 ppb Hg and 1 ppb Cd stabilized with 1% nitric acid. Reserve 50 mL
for Calibration solution 1. Bring 50 mL of Calibration solution 1 to 100 mL. Reserve
50 mL for Calibration solution 2. Calibration solution 3 was adjusted to account for
the lower target levels in Table 1. A similar dilution as the previous scheme could be
used.
Experiment: Analytical Method and
Conditions
Table 3: Calibration Solutions
Table 2: Measurement Conditions
Results and Conclusion
Fig 2: Arsenic Calibration Curve
Figures 2, 3, 4 and 5 show the generated calibration curves for each of the analytes.
All calibration curves achieved a good linear coefficient of 0.999 or better, showing
the instrument is capable of measuring the specified target range shown in Table 1
and Table 3.
Fig 3: Cadmium Calibration Curve
Results and Conclusion
Fig 4: Lead Calibration Curve Fig 5: Mercury Calibration Curve
Figures 6 and 7 shows the signals of each analyte of the unknown samples and
that of the spikes for As, Cd, Hg and Pb. There is good signal distinction at each
of the target analysis levels indicated in Table 1.
Fig 6: Arsenic & Cadmium Sample and Spike
Results and Conclusion
Fig 7: Lead & Mercury Sample and Spike
Results and Conclusion
Table 4: Results of
Sample & Spike
The results in Table 4 show that all of the elements were within the target analysis
and the sample spikes achieved recoveries of 90%-110% of their theoretical
values. The recoveries show that the system is capable achieving good sensitivity
and accuracy at the desired elemental concentration levels.
Need More Info?
Thank you for viewing this presentation. Should you have any
questions or require additional information about our research,
products, or services, please visit our Web site at:
www.ssi.shimadzu.com
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Analysis of “The Big Four” Heavy Metals in Hops by Graphite Furnace Atomic Absorption and Cold Vapor Mercury

  • 1. Analysis of “The Big Four” Heavy Metals in Hops by Graphite Furnace Atomic Absorption and Cold Vapor Mercury Robert H. Clifford, Dan Davis, Keith Long, and Justin Masone, Shimadzu Scientific Instruments, Columbia, MD, USA
  • 2. Introduction Plants concentrate metals by absorbing them from the soil in which they are grown. Some metals are beneficial and essential for life whereas other metals are highly toxic and have negative effects with even the lowest of levels. Because of their toxicity, quantification of these elements is needed. This application will investigate the preparation and analysis for heavy metals in Cascade Hops using Shimadzu AA-7000 with Graphite Furnace Atomic Absorption and Cold Vapor techniques. Spike and Recovery tests are performed at or below the analysis target levels to ensure accuracy and sensitivity of the technique. Element Analysis Target PPM As Prepped (50x dil.) PPB Lead 1.20 24 Cadmium 0.82 16 Mercury 0.40 8.0 Arsenic 2.00 40 Table 1. Metals Target Analysis
  • 3. Cascade Hops were purchased pre-dried and ground. 0.5 grams of Hops were added to a closed vessel digester, and 4 mL of Nitric Acid, 2 mL of 30% H2O2, and 1 mL of DI H2O were added. The sample was ramped to 900 watts over 15 minutes and held for another 20 minutes at that power. The sample was then allowed to cool and brought to 25 mL total volume with DI H2O. 2 mL of the solution was reserved for analysis of Cd, As and Pb by Graphite Furnace Atomic Absorption. 20 mL of sample was reserved for Hg analysis by Cold Vapor; 10 mL of untreated sample, and 10 mL of sample spiked to 1 ppb Hg. Experiment: Sample Preparation
  • 4. Fig. 1: Digestion/Preparation Procedure Shimadzu AA-700 Experiment: Sample Preparation
  • 5. Experiment: Analytical Method and Conditions Measurement was conducted using the calibration curve method. The main measurement parameters of the instrument are shown in Table 2. The standard solutions were prepared by diluting commercially available standard solutions for atomic absorption measurement. 100 mL of calibration solution was prepared at 20 ppb As, Pb, 10 ppb Hg and 1 ppb Cd stabilized with 1% nitric acid. Reserve 50 mL for Calibration solution 1. Bring 50 mL of Calibration solution 1 to 100 mL. Reserve 50 mL for Calibration solution 2. Calibration solution 3 was adjusted to account for the lower target levels in Table 1. A similar dilution as the previous scheme could be used.
  • 6. Experiment: Analytical Method and Conditions Table 3: Calibration Solutions Table 2: Measurement Conditions
  • 7. Results and Conclusion Fig 2: Arsenic Calibration Curve Figures 2, 3, 4 and 5 show the generated calibration curves for each of the analytes. All calibration curves achieved a good linear coefficient of 0.999 or better, showing the instrument is capable of measuring the specified target range shown in Table 1 and Table 3. Fig 3: Cadmium Calibration Curve
  • 8. Results and Conclusion Fig 4: Lead Calibration Curve Fig 5: Mercury Calibration Curve
  • 9. Figures 6 and 7 shows the signals of each analyte of the unknown samples and that of the spikes for As, Cd, Hg and Pb. There is good signal distinction at each of the target analysis levels indicated in Table 1. Fig 6: Arsenic & Cadmium Sample and Spike Results and Conclusion Fig 7: Lead & Mercury Sample and Spike
  • 10. Results and Conclusion Table 4: Results of Sample & Spike The results in Table 4 show that all of the elements were within the target analysis and the sample spikes achieved recoveries of 90%-110% of their theoretical values. The recoveries show that the system is capable achieving good sensitivity and accuracy at the desired elemental concentration levels.
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