Page 10 - Shimadzu Journal vol.3 Issue1
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Environmental Analysis




            The headspace autosampler can be transferred to a GC-MS for   8. Acknowledgments
            identification of unknown compounds detected by HS-GC-FID.
                                                               The authors would like to thank the Shimadzu Institute for
            Analysis of compounds with a boiling point significantly higher
                                                               Research Technology (SIRT) and the Shimadzu Center for
            than 90 °C may not be suitable for headspace sampling.
                                                               Advanced Analytical Chemistry (SCAAC) at The University of Texas
             Analysis Conditions                               at Arlington for use and support of the aforementioned analytical
                                                               instruments. They would also like to thank Shimadzu Scientific
             Instrument: GC-2010 Plus
                                                               Instruments, Inc. (Columbia MD) for the use of the TOC
             Column: ZB-BAC2, 30 m L. x 0.32 mm I.D., df:1.2 µm
                                                               instrument featured in this work.
             Column oven temp.: 40 °C (4.5 min.) ˠ (30 °C/min.) ˠ130 °C (2 min.)
                                                       ˠ(35 °C/min.) ˠ200 °C (0.5 min.))  9. References
             Carrier gas: He                FID temp.: 200 °C  1  US EPA. Drinking Water Contaminants.
             Carrier gas control: Linear velocity,    Agitator temp.: 90 °C  http://water.epa.gov/drink/contaminants/index.cfm#one
                                          50 cm/s  Agitator time: 15 min.  (accessed October 28, 2014).
             Split ratio: 10:1              Syringe temp.: 90 °C  2  US EPA. Private Drinking Water Wells.
             Injection port temp.: 200 °C                        http://water.epa.gov/drink/info/well/ (accessed October 28,
             Injection volume: 750 µL                            2014).
                                                               3  Fontenot, B. E.; Hunt, L. R.; Hildenbrand, Z. L.; Carlton, D. D.,
            6. TOC/ TN                                           Jr.; Oka, H.; Walton, J. L.; Hopkins, D.; Osorio, A.; Bjorndal, B.;
                                                                 Hu, Q. H.; Schug, K. A. An Evaluation of Water Quality in
            Carbon and nitrogen content of the water were measured with
                                                                 Private Drinking Water Wells Near Natural Gas Extraction Sites
            the Shimadzu TOC-L outfitted with the TNM-L total nitrogen
                                                                 in the Barnett Shale Formation. Environ. Sci. Technol. 2013, 47,
            module. Samples were filtered with a 0.45 µm PTFE Luer lock
                                                                 10032-10040.
            syringe filter as needed and filled a 40 mL volatile organic analysis
                                                               4  Almasri, M. N.; Kaluarachchi, J. J. Modeling Nitrate
            autosampler vial.  Total Carbon (TC), Inorganic Carbon (IC),
            Nonpurgable Organic Carbon (NPOC), Purgable Organic Carbon   Contamination of Groundwater in Agricultural Watersheds. J.
            (POC), and Total Nitrogen (TN) were measured. When TC-IC was   Hydrol. 2007, 343, 211-229.
            below 2 ppm, NPOC+POC was used for reporting TOC per   5  Boyer, E.W.; Clark, J.; Madden, M.; Rizzo, D.E. The impact of
            manufacturer suggestions. In all other cases, TC-IC was used for   Marcellus gas drilling on rural drinking water supplies.  The
            TOC.                                                 Center for Rural Pennsylvania. 2012.
            TOC and TN are valuable to validate the presence of organic
            compounds and amines or other nitrogen-containing organic
            compounds determined by a more detailed analytical method. A
            non-zero TN value does not confirm nitrogen-containing organic
            compounds, as TN is also sensitive to nitrate, nitrite, and ammonia.
            Agricultural contamination of groundwater results primarily in an
                                                        4
            increase of halogenated and nitrogen-containing compounds ,
            while UOG contamination would result in the introduction of
            carbon or carbon and nitrogen-containing compounds, depending
            on the phase of the extraction operation. The detection of
            compounds GC-MS/ HS-GC-FID should be accompanied by
            nonzero TOC values. Many caveats such as analyte response
            factors and volatility, can account for the lack of graphical linearity
            of the GC and TOC measurements from sample to sample.
            In addition to validating more targeted analytical methods, TOC/
            TN can be utilized as an indicator for contaminated groundwater
                   5
            samples.  It may be efficient to screen many samples with TOC/ TN
            before applying more detailed and costly methods. A positive
            correlation between HS-GC-FID and TOC data was found for an
            arbitrary set of 14 groundwater samples selected for evaluation.
            Four out of five of the samples with the highest total HS-GC-FID
            peak areas had the highest TOC/ NPOC values.

            7. Summary
            Research involving the chemical analysis of groundwater is likely to
            be highly scrutinized due to the potential for risks associated with
            health and environmental impacts. Although the measurement of
            general parameters such as conductivity and Total Organic Carbon
            (TOC) may have analytical utility on their own, they can be even more
            valuable for supporting findings using more targeted analytical
            techniques such as ICP-OES and GC-MS.



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