The Determination of Polychlorinated Biphenyls (PCB) Using EPA Method 8082
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This application note discusses the analysis of polychlorinated biphenyls (PCBs) using EPA Method 8082, highlighting the challenges in quantification due to the complex mixtures of aroclors. It details a method leveraging electron capture detection (ECD) for the identification and quantification of specific PCB congeners, particularly aroclor 1016 and aroclor 1260, while emphasizing the effective use of Waters® Empower® 3 software for peak selection and quantitation. The results demonstrate the method's applicability and accuracy, confirming the software's capability to handle analytes in complicated matrices efficiently.
The Determination of Polychlorinated Biphenyls (PCB) Using EPA Method 8082
- 1. A P P L I C A T I O N N O T E Author: David Scott PerkinElmer, Inc. Shelton, CT Gas Chromatography Introduction Polychlorinated biphenyls (PCB) are considered persistent organic pollutants under the Stockholm Convention of Persistent Organic Pollutants and have not been manufactured in the U.S. since they were banned in 1979. They are relatively chemically inert and do not decompose readily, being resistant to oxidation, and are only very slightly soluble in water. Prior to being banned, PCBs were widely used in closed systems such as electrical transformers, capacitors and as heat transfer fluids. They were also used in adhesives, paint, plasticizers and machining oils. Production in the U.S. was wholly from the Monsanto company, who manufactured PCBs under the name Aroclor from 1930 to 1977, using a naming scheme that generally followed a four number convention with the first two digits the number of carbons and the last two digits the percentage of chlorine by mass. Aroclor 1260 (12 carbons and 60% chlorine by mass) was used in electrical equipment up until 1950, when it was replaced by Aroclor 1242 through the next 20 years, until Aroclor 1016 (12 carbons and 42% chlorine) was produced. The Determination of Polychlorinated Biphenyls (PCB) Using EPA Method 8082
- 2. 2 In all cases the Aroclor sold was a mixture of 209 congeners that can result in a challenging separation and quantitation. There are two main options for detection at the required limits of quantitation; typically Mass Spectrometry (MS) or Electron Capture Detection (ECD). This paper describes the application of an ECD for the quantitation and identification of the PCBs found in Aroclor 1260 and Aroclor 1016. The Environmental Protection Agency (EPA) has released method 8082 for the analysis of PCBs as Aroclors, having tested the method against a select group of 19 congeners common to many Aroclor mixtures. The analysis of Aroclors and PCBs is complicated by matrix effects and the method allows the analysis of Aroclors, using those selected congeners, and also enables the analysis of other PCBs if appropriate quality controls are in place. Capillary Injector 225°C Electron Capture Detector 300°C 60 ml/min Nitrogen make up Oven Program 150°C (Hold 1 min) Ramp 25°C/min 280°C (Hold 0.6 min) Ramp 35°C/min 315°C (Hold 0 min) Analytical column Elite CLP 15 m x 0.530 mm x 0.5 µm Experimental Figure1.Standard chromatogram of mixed Aroclor 1016 and Aroclor 1260. Figure 2. Custom calculation to establish the Average RF for the detailed reference component. A splitless injection was performed with 1 µL injected into a 4 mm SGE deactivated single taper liner without glass wool. Results A standard typical Aroclor chromatogram is shown in Figure 1. A standard containing Aroclor 1016 and Aroclor 1260 will contain many of the peaks that are present in other Aroclor samples. The analyst therefore calibrates on EPA Method 8082 to cover the broad range of available congeners and it should be noted that it is also possible to use EPA Method 8082 for other congeners if appropriate resolution and reporting steps are completed. The method requires that a five point calibration is obtained for linearity and to establish the response factor (RF) for a minimum of 5 peaks from each Aroclor. The calibration curve generated was from standards of 0.025, 0.05, 0.2, 0.4, and 0.8 µg/mL prepared from a commercial stock standard diluted in iso-octane. The RF for each analyte is automatically calculated for each injection and it is possible to create a custom calculation using the Waters® Empower® 3 software that will average the RF for each analyte based on the calibration curve. An additional custom field will then calculate the amount from the peak area and Average RF as described in Figure 3. mV 40.00 45.00 50.00 55.00 60.00 Minutes 1.50 2.00 2.50 3.00 3.50 4.00 4.50 5.00 5.50 Aroclor1016peak1 Aroclor1016peak2 Aroclor1016peak3 Aroclor1016peak4 Aroclor1016peak5 Aroclor1016peak6 Aroclor1016peak7 Aroclor1016peak8 Aroclor1260peak1 Aroclor1260peak2 Aroclor1260peak3 Aroclor1260peak4 Aroclor1260peak5 Aroclor1260peak6 Aroclor1260peak7 Aroclor1260peak8 Aroclor1260peak9 Aroclor1260peak10 Aroclor1260peak11 Aroclor1260peak12 Aroclor1260peak13 Aroclor1260peak14 Table1.GC conditions: Clarus® 580 GC.
- 3. 3 The requirements of EPA Method 8082 are to quantify on three to five selected peaks. The Empower® 3 software integrates all of the standard peaks, therefore only one integration method is required. The analyst can then filter the Result table for those peaks that are not compromised by other Aroclors or matrix effects to obtain the correct result. Filtering is achieved in the report result table by simply selecting the analytes of interest in the data filtering option shown in Figure 5. Initially all of the analytes are present in the report before the analyst filters the peaks of interest. Figure3.Calculated_Amount now entered as a custom calculation. Figure4.All analytes are present in the initial report. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 Peak Name Processed Channel Retention Time (min) Area Height Calculated Amount (ng) Aroclor 1016 peak 1 Aroclor 1016 peak 2 Aroclor 1016 peak 3 Aroclor 1016 peak 4 Aroclor 1016 peak 5 Aroclor 1016 peak 6 Aroclor 1016 peak 7 Aroclor 1016 peak 8 Aroclor 1016 peak 9 Aroclor 1260 peak 1 Aroclor 1260 peak 2 Aroclor 1260 peak 3 Aroclor 1260 peak 4 Aroclor 1260 peak 5 Aroclor 1260 peak 6 Aroclor 1260 peak 7 Aroclor 1260 peak 8 Aroclor 1260 peak 9 Aroclor1260 peak 10 Aroclor 1260 peak 11 Aroclor 1260 peak 12 Aroclor 1260 peak 13 Aroclor 1260 peak 14 Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B Channel B 1.836 2.141 2.299 2.512 2.618 2.661 2.781 2.937 3.003 3.908 4.003 4.190 4.295 4.418 4.512 4.611 4.692 4.813 4.914 5.317 5.476 5.638 5.743 9352 13335 10121 24688 11046 9142 15257 10372 11165 14081 1925 28715 11063 30541 18900 6202 24172 3094 52944 8550 16116 5746 728 2675 4345 3358 7893 4572 3752 3790 4207 3195 5699 858 10528 4851 11245 9057 2596 8133 1661 23931 4425 8700 3176 422 0.106 0.106 0.105 0.107 0.109 0.107 0.109 0.109 0.108 0.108 0.014 0.109 0.109 0.109 0.110 0.106 0.108 0.106 0.108 0.108 0.109 0.113 0.108 All Aroclor peaks Processed Channel: Channel B
- 4. 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. 012227_01 PKI PerkinElmer, Inc. 940 Winter Street Waltham, MA 02451 USA P: (800) 762-4000 or (+1) 203-925-4602 www.perkinelmer.com Figure6.Aroclor 1016 peaks selected and averaged. 1 2 3 4 5 Mean PeakName Processed Channel Retention Time (min) Area Height Calculated Amount (ng) Aroclor 1016 peak1 Aroclor 1016 peak5 Aroclor 1016 peak6 Aroclor 1016 peak7 Aroclor 1016 peak9 Channel B Channel B Channel B Channel B Channel B 1.836 2.618 2.661 2.781 3.003 9352 11046 9142 15257 11165 2675 4572 3752 3790 3195 0.106 0.109 0.107 0.109 0.108 0.108 Aroclor 1016 Results Processed Channel: Channel B Figure7.Aroclor 1260 peaks selected and averaged. 1 2 3 4 5 Mean PeakName Processed Channel Retention Time (min) Area Height Calculated Amount (ng) Aroclor 1260 peak3 Aroclor 1260 peak4 Aroclor 1260 peak5 Aroclor 1260 peak7 Aroclor 1260 peak9 Channel B Channel B Channel B Channel B Channel B 4.190 4.295 4.418 4.611 4.813 28715 11063 30541 6202 3094 10528 4851 11245 2596 1661 0.109 0.109 0.109 0.106 0.106 0.107 Aroclor 1260 Results Processed Channel: Channel B Having the ability to selectively choose the best peaks that contain the least matrix interference or overlap from other Aroclors, allows for more accurate quantitation of the chosen analytes. This selection process is fast and easy and does not require further processing. The five peaks selected are then analyzed in the report for the final quantification result. A 100 µg/mL standard was prepared and analyzed to validate the calculations and the result was determined to be within 10% of the expected value showing the applicability of the instrument and calculations. Conclusion The Empower® 3 chromatography data software (CDS) can easily complete the calculations of EPA Method 8082 with a rapid and simple filtering of the result table by analyte name, easily quantifying samples that are in a challenging matrix. No separate integration is required which decreases the analyst work load and increases productivity. Figure5.Entering the filter conditions, selecting the peaks by name.