Explosives detection in soil using a field-portable continuous flow immunosensor
Introduction
Field screening methods to detect environmental contaminants continue to proliferate as microelectronics improve and analytical instruments become miniaturized. One application of on-site testing can be seen in the identification, characterization, and remediation of sites contaminated with 2,4,6-trinitrotoluene (TNT) and hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX). These energetic compounds pose a serious site characterization, cleanup, and monitoring problem for the Department of Defense (DoD), Environmental Protection Agency (EPA), and other government institutions. The compounds are most commonly encountered in contaminated soils in close proximity to facilities used to manufacture, assemble, test, store, and demilitarize munitions. Once deposited, they do not rapidly decompose and will leach through soils into the groundwater, creating a serious environmental hazard (Spalding et al. [1]).
The current method of choice for analysis of nitroaromatics and nitroamines is the US EPA Method 8330 utilizing HPLC (Crockett et al. [2], SW-846 [3], Jenkins et al. [4]). Though laboratory analyses provide a more complete, exact profile of contaminants present in a given sample than most field methods, remediation goals require a large number of samples to be run at infrequent intervals. It is difficult, costly and time-consuming to send samples off-site for testing. With rigorous sampling plans and careful attention to QA/QC, accuracy, and precision, on-site methods provide real-time information to remediation managers that can improve decision-making, allow better risk assessments, and significantly decrease analytical costs.
There are a number of analytical laboratory methods available for detection of TNT and RDX including thin-layer chromatography (Douse [5], Haas et al. [6]), capillary electrophoresis (Northrop et al. [7], Oehrle [8], [9]), liquid chromatography (Nair and Huber [10], Hirata and Okamoto [11], Bauer et al. [12], Kleibohmer et al. [13]), ion exchange resin based tube sensor (Heller et al. [14]), and PVC membrane-based sensor (Zhang and Seitz [15]), GC/MS, HPLC (Kolla [16], Yinon and Zitrin [17], Jenkins et al. [18], Caton and Griest [19]). These laboratory methods are often cost prohibitive, time consuming, and labor intensive for use in a field screening application. In the early 1990s, Jenkins and Walsh [20] pioneered a field method for the detection of explosives using a colorimetric technique employing the Janovsky reaction. Since then, several qualitative and quantitative methods have been validated and commercialized for on site testing, including the D-Tech field test kit (Strategic Diagnositics [21], [23]), Ensys immunoassay kit, (Ensys Environmental Products [22]) and other immunochemical based methods (Shriver-Lake et al. [24], [25], Narang et al. [26], [27]). In general, field measurements are considered to be useful for screening purposes, providing reliable data and timely information on the extent of contamination or remediation progress. Assays utilizing immunological reactions to detect a variety of analytes have been well studied (Keuchel et al. [28], [29], [30], Whelan et al. [31], Narang et al. [26], [27]). This report demonstrates the effectiveness of the FAST 2000, a commercially available field version of the continuous flow immunosensor (CFI), for detection of TNT and RDX in soil samples obtained from environmental cleanup sites.
Section snippets
Antibodies and standards
The 11B3 monoclonal antibody specific for TNT (Whelan et al. [31]) and monoclonal anti-RDX (IgG 50518 from Strategic Diagnostics Inc., Newark, DE) were used. Antibodies were immobilized on Porous Immunodyne ABC membranes (Pall Corp., Port Washington, NY), 5.0 μm pore size according to manufacturer’s instructions. System buffer used in the analyses was 10 mM sodium phosphate, 0.01% Tween 20, and 2.5% ethanol, pH 7.4. Analytical standards of 2,4,6-trinitrotoluene (TNT) and
Laboratory standards
Experiments were performed using standards of the explosives prepared in the system buffer. Table 1 lists the results of the accuracy and precision tests that demonstrate a high degree of accuracy between RDX and TNT, with values that range from 93 to 99%. The precision of the sensor was also calculated, with percentages that range from 6 to 15%. Using the criteria outlined in the methods, the instrument is capable of a detection limit of 10 μg/l in system flow buffer. Fig. 2 is included to
Conclusion
Overall, the NRL biosensor performance suggests that the FAST 2000 instrument is a promising field technology for determinations of explosives in soil. The instrument is simple to use, requires minimal sample preparation, is easily carried to the field and generates minimal waste. Determinations of TNT and RDX levels were accurate and precise down to 10 μg/l in system buffer, with acceptable levels of false positive/false negative values. We found that the highly heterogeneous nature of soils
Acknowledgements
The authors thank Drs. Eddie Chang and Harold Goldston for review of the manuscript and Drs. Harry Craig and Tom Jenkins for their technical support. This work was funded by the Environmental Security and Technology Certification Program. The views expressed here are those of the authors and do not represent those of the Department of the Navy or the Department of Defense.
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