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Authors:
Kathryn Lawson-Wood
Ian Robertson
PerkinElmer, Inc.
Seer Green, England
Introduction
Chromium occurs in
water systems in two
forms, Cr(III) and Cr(VI).
Cr(VI) is of particular
interest due to its known
carcinogenic nature. In this application, the quantitative analysis of Cr(VI) was
accomplished using the LAMBDA™
265 UV/Vis spectrophotometer and Merck
Spectroquant®
chromate cell test. The method is analogous to APHA 3500-Cr
B and DIN 38405-24 and is USEPA approved for wastewater.
Principle
Chromium (VI) ions react with diphenylcarbazide in weakly phosphoric
solution. The product, diphenylcarbazone, is a red-violet complex which can be
detected photometrically at 550 nm. The chromate cell test kit is suitable for the
concentration range of 0.11 – 4.46 mg/L chromate allowing the concentration of
chromium(VI) in a water sample to be determined without the use of a calibration
curve by multiplying the measured absorbance at 550 nm with a known factor.
Water Analysis Using
LAMBDA UV/Visible
Spectrophotometers: Hexavalent
Chromium Determination
A P P L I C A T I O N N O T E
UV/Visible Spectroscopy
2
Reagents and Apparatus
1.	Merck Spectroquant®
chromate cell test kit – (1.14552.0001)
containing reaction cells and reagent Cr-3K
2.	 PerkinElmer LAMBDA 265 PDA UV/Visible Spectrophotometer
3.	 UV Lab™
software
4.	 Cuvettes (10 mm pathlength)
5.	Chromium(VI) concentrate 1.00 g Cr(VI) for 1 L standard
solution (2.23 g/L chromate)
6.	 Deionised (DI) water
7.	 Volumetric flasks (1 L and 100 ml)
8.	Micropipettes
Method
A stock solution of chromate (2.23 g/L) was prepared in a one
litre volumetric flask and diluted with DI water. From this stock
solution, a 2.07 mg/L chromate solution was prepared in a 100 ml
volumetric flask by dilution with DI water.
Following preparation of solutions, 6 drops of Cr-3K were placed
in a reaction cell. The cell was then closed, shaken and left to
stand for one minute. Using a pipette, 5.0 ml of the 2.07 mg/L
chromate solution was added to the reaction cell, shaken and left
to stand for a further minute. This technique was also carried out
for the blank which instead used DI water.
Using the UV Lab software, the LAMBDA 265 instrument
parameters were set, as shown in Figure 1, to measure the
absorbance at 550 nm, and an equation set up to calculate the
chromate concentration as shown in Equation 1. Following
measurement of the blank, the known chromate solution in
the reaction cell was transferred into a 10 mm cuvette and the
absorbance recorded.
Equation 1.
Chromate concentration (mg/L) = A550 * 2.92
Results
Figure 2 shows spectra from 5 repeat runs of the 2.07 mg/L
chromate sample, with the results shown in Table 1. The mean
absorbance at 550 nm was determined to be 0.713, corresponding
to a calculated concentration of 2.08 mg/L chromate. The results
obtained had a high level of accuracy and repeatability with a
relative standard deviation of 0.1%.
Figure1.Instrumentparametersandmethodsetup.
Figure2.OverlaidUV/Visspectraofrepeatmeasurementsofchromatesolution.
For a complete listing of our global offices, visit www.perkinelmer.com/ContactUs
Copyright ©2015, PerkinElmer, Inc. All rights reserved. PerkinElmer®
is a registered trademark of PerkinElmer, Inc. All other trademarks are the property of their respective owners.
012452A_01	PKI
PerkinElmer, Inc.
940 Winter Street
Waltham, MA 02451 USA	
P: (800) 762-4000 or
(+1) 203-925-4602
www.perkinelmer.com
Table1.Resultsforrepeatmeasurements.
Chromate
Solution
Absorbance
at 550 nm
Chromate
Concentration (mg/L)
Repeat 1 0.714 2.08
Repeat 2 0.713 2.08
Repeat 3 0.712 2.08
Repeat 4 0.713 2.08
Repeat 5 0.712 2.08
Conclusion
Quantitative analysis of chromium(VI) in water was achieved
rapidly with a high level of repeatability and accuracy using the
LAMBDA 265 UV/Vis spectrophotometer and UV Lab software.
The chromate cell test kit requires no complex preparation of
chemical solutions and allows simple determination of chromate
concentration, without the preparation and measurement of
calibration standards.

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Determination of Hexavalent Chromium Using UV/Vis Spectrophotometry

  • 1. Authors: Kathryn Lawson-Wood Ian Robertson PerkinElmer, Inc. Seer Green, England Introduction Chromium occurs in water systems in two forms, Cr(III) and Cr(VI). Cr(VI) is of particular interest due to its known carcinogenic nature. In this application, the quantitative analysis of Cr(VI) was accomplished using the LAMBDA™ 265 UV/Vis spectrophotometer and Merck Spectroquant® chromate cell test. The method is analogous to APHA 3500-Cr B and DIN 38405-24 and is USEPA approved for wastewater. Principle Chromium (VI) ions react with diphenylcarbazide in weakly phosphoric solution. The product, diphenylcarbazone, is a red-violet complex which can be detected photometrically at 550 nm. The chromate cell test kit is suitable for the concentration range of 0.11 – 4.46 mg/L chromate allowing the concentration of chromium(VI) in a water sample to be determined without the use of a calibration curve by multiplying the measured absorbance at 550 nm with a known factor. Water Analysis Using LAMBDA UV/Visible Spectrophotometers: Hexavalent Chromium Determination A P P L I C A T I O N N O T E UV/Visible Spectroscopy
  • 2. 2 Reagents and Apparatus 1. Merck Spectroquant® chromate cell test kit – (1.14552.0001) containing reaction cells and reagent Cr-3K 2. PerkinElmer LAMBDA 265 PDA UV/Visible Spectrophotometer 3. UV Lab™ software 4. Cuvettes (10 mm pathlength) 5. Chromium(VI) concentrate 1.00 g Cr(VI) for 1 L standard solution (2.23 g/L chromate) 6. Deionised (DI) water 7. Volumetric flasks (1 L and 100 ml) 8. Micropipettes Method A stock solution of chromate (2.23 g/L) was prepared in a one litre volumetric flask and diluted with DI water. From this stock solution, a 2.07 mg/L chromate solution was prepared in a 100 ml volumetric flask by dilution with DI water. Following preparation of solutions, 6 drops of Cr-3K were placed in a reaction cell. The cell was then closed, shaken and left to stand for one minute. Using a pipette, 5.0 ml of the 2.07 mg/L chromate solution was added to the reaction cell, shaken and left to stand for a further minute. This technique was also carried out for the blank which instead used DI water. Using the UV Lab software, the LAMBDA 265 instrument parameters were set, as shown in Figure 1, to measure the absorbance at 550 nm, and an equation set up to calculate the chromate concentration as shown in Equation 1. Following measurement of the blank, the known chromate solution in the reaction cell was transferred into a 10 mm cuvette and the absorbance recorded. Equation 1. Chromate concentration (mg/L) = A550 * 2.92 Results Figure 2 shows spectra from 5 repeat runs of the 2.07 mg/L chromate sample, with the results shown in Table 1. The mean absorbance at 550 nm was determined to be 0.713, corresponding to a calculated concentration of 2.08 mg/L chromate. The results obtained had a high level of accuracy and repeatability with a relative standard deviation of 0.1%. Figure1.Instrumentparametersandmethodsetup. Figure2.OverlaidUV/Visspectraofrepeatmeasurementsofchromatesolution.
  • 3. For a complete listing of our global offices, visit www.perkinelmer.com/ContactUs Copyright ©2015, PerkinElmer, Inc. All rights reserved. PerkinElmer® is a registered trademark of PerkinElmer, Inc. All other trademarks are the property of their respective owners. 012452A_01 PKI PerkinElmer, Inc. 940 Winter Street Waltham, MA 02451 USA P: (800) 762-4000 or (+1) 203-925-4602 www.perkinelmer.com Table1.Resultsforrepeatmeasurements. Chromate Solution Absorbance at 550 nm Chromate Concentration (mg/L) Repeat 1 0.714 2.08 Repeat 2 0.713 2.08 Repeat 3 0.712 2.08 Repeat 4 0.713 2.08 Repeat 5 0.712 2.08 Conclusion Quantitative analysis of chromium(VI) in water was achieved rapidly with a high level of repeatability and accuracy using the LAMBDA 265 UV/Vis spectrophotometer and UV Lab software. The chromate cell test kit requires no complex preparation of chemical solutions and allows simple determination of chromate concentration, without the preparation and measurement of calibration standards.