Aerial view of the Warren, Maine lagoon system. Photo courtesy of Woodard and Curran.

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Mars Hill Wastewater Lagoon System - Mars Hill  Maine. Photo Courtesy of Wright-Pierce Engineers.
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Colorimetry

 

by Tim Loftus

 

            Do you test for phosphorus, residual chlorine, or ammonia-nitrogen in your laboratory? If so, you most likely use colorimetric procedures to analyze for some of, if not all of them. The principles of colorimetric analysis can also be used to determine many other parameters in the wastewater and water field, including metal analyses and the nitrate/nitrite series.
 

            The idea behind colorimetry is very simple. But first here is a simplistic review of color: most substances absorb at least a little bit of light. Black objects absorb all the colors of the rainbow and reflect little light. White objects absorb almost no color and reflect all the colors of the rainbow (called white light). In between, most objects absorb some light and reflect the rest. That is how we see different colors – a red object absorbs all the light except the red wavelength, which reflects off the subject and appears red to us. Similarly, a blue object absorbs all the light except the blue wavelength. In reality, though, most colors we see are blends of several wavelengths being reflected back to us.
 

            We can use this principle of color reflection and absorption to determine the concentration of a chemical in solution (like residual chlorine in water). There are two ways this has typically been done; one uses Nessler tubes (these look like test tubes) or a color wheel and the other uses a spectrophotometer. In both cases the substance you want to determine the concentration of needs to be color-enhanced by reacting it with a specific chemical. In the case of phosphorus analysis, the phosphorus is reacted with ammonium molybdate, potassium antimonyl tartrate, and ascorbic acid to form a blue color; residual chlorine is reacted with DPD to form a red color; and ammonia-nitrogen is reacted with Nessler reagent for form a yellow to brownish-yellow color.
 

            While each procedure has its own specific limitations, the intensity of the color for each parameter is proportional to its concentration. Here’s a simplified example to make this point clear: if a phosphorus sample has twice the blue color intensity as another sample of phosphorus, the first sample has twice the concentration of phosphorus as the second sample.
 

            In using Nessler tubes, a series of standard solutions is made and reacted with its specific color-enhancing chemical. Then the sample in question is color-enhanced and compared to the standards. From this the concentration of the sample is determined.  Note that the color wheels of years ago worked on this same idea. Rather than making a series of standards to compare color intensity, these colors were printed on a wheel or card to which the liquid sample would be compared. Both of these were very subjective tests, although easy and quick to use in the field. Today, neither the use of Nessler tubes nor color wheels are approved for NPDES reporting purposes.
 

            A spectrophotometer works by a similar principle. But rather than measuring the intensity of the reflected light (the color your see) as with Nessler tubes, it measures the amount of a particular wavelength that is absorbed by the sample. Usually the best wavelength to use is the visible color’s complement. For example, if a color-enhanced sample is red, a wavelength in the green part of the spectrum is used in a spectrophotometer. The amount of this wavelength that is absorbed by the sample is proportional to its concentration.
 

            There are, however, limitations to colorimetry. Samples must be diluted or occasionally concentrated so that a valid measurement can be made since the workable range often falls within only a few milligrams per liter. Sometimes non-target substances react with the color-enhancing chemicals to create a false positive reading, although test procedures are generally good at listing these interferences and describe ways to counteract or reduce their effects. Other interferences include bubbles in the sample cells or tubes, turbidity of the sample, and sample color (the wastewater from a textile dying process, for example, is nearly impossible analyze using colorimetric methods). Fingerprints on the sample cells and optically mismatched sample cells will also give erroneous readings.
 

            Despite the challenges of colorimetry, it remains an easy-to-use and accurate test if care is taken to match the sample with the method limitations, the equipment is clean and in proper working order, and a good quality assurance plan is in place to indicate that the results are accurate.
 

            If you have any questions, suggestions, or comments, contact NEWEA Lab Practices Committee Chair Tim Loftus at (508) 949-3865 timloftus@msn.com. For more information on the NEWEA Laboratory Practices Committee, please contact Tim Loftus or Elizabeth Cutone, NEWEA Executive Director, 100 Tower Office Park, Woburn, MA 01801, (781) 939-0908, ecutone@newea.org.
 

 

 

 

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