Separation and enrichment of traces of explosives and their by-products from water by multiple micro liquid extraction for their determination by capillary gas chromatography

High-speed fluorescence detection of explosives-like vapors

In this paper, we report on the preparation of novel cross-reactive optical microsensors for high-speed detection of low-level explosives and explosives-like vapors. Porous silica microspheres with an incorporated environmentally sensitive fluorescent dye are employed in high-density sensor arrays to monitor fluorescence changes during nitroaromatic compound (NAC) vapor exposure. The porous silica-based sensor materials have good adsorption characteristics, high surface areas, and surface functionality to help maximize analyte-dye interactions. These interactions occur immediately upon vapor exposure, i.e., in less than 200 ms and are monitored with a high-speed charge-coupled device camera to produce characteristic and reproducible vapor response profiles for individual sensors within an array. Employing thousands of identical microsensors permits sensor responses to be combined, which significantly reduces sensor noise and enhances detection limits. Normalized response profiles for 1,3-dinitrobenzene (1,3-DNB) are independent of analyte concentration, analyte exposure time, or sensor age for an array of one sensor type. Explosives-like NACs such as 2,4-dinitrotoluene and DNB are detected at low part-per-billion levels in seconds. Sensor-analyte profiles of some sensor types are more sensitive to low-level NAC vapor even when in a higher organic vapor background. We show that single-element arrays permit the detection of low-level nitroaromatic compound vapors because of sensor-to-sensor reproducibility and signal averaging.

Improvement of EPA method 8330: complete separation using a two-phase approach

Complete separation of the 14 nitroaromatic and nitramine analytes targeted in EPA Method 8330 was achieved using a 30 x 4.6 mm Bondesil CN guard column in series with a 250 x 4.6 mm Bondesil C18 column (5 microns particles). Consistent with Method 8330 specifications, the mobile phase in the separation was 1:1 methanol:water and the flow-rate was 1.5 ml min-1. The success of this two-phase system proved to be largely a consequence of the unique resolution afforded by the Bondesil C18 column: complete separation of the 14 explosives could not be achieved using other CN/C18 column combinations. Additionally, while Method 8330 calls for a 100-microliter injection loop, separation on the Bondesil CN/C18 system was possible only using a 20-microliter injection loop. The loss of resolution with larger injection volume appears to be a result of the injection solvent, methanol, modifying the composition of the mobile phase both in the CN guard column and in the initial portion of the C18 column. The current method nevertheless represents an improvement over Method 8330, which calls for both a screening and confirming analysis. By separating the 14 Method 8330 analytes in a single run, the two-phase approach can increase sample throughput by decreasing analysis times.

Gas chromatographic determination of aromatic amines in water samples after solid-phase extraction and derivatization with iodine. II. Enrichment

A procedure for the enrichment of aromatic amines via solid-phase extraction was developed. A HR-P phase based on styrene-divinylbenzene was used for the investigations, generally followed by derivatization with iodine and determination via GC-ECD. The recoveries of 53 aromatic amines in a drinking water matrix at pH 9 were determined. Most anilines showed relative recoveries between 80-120% with relative standard deviations of< or = 5% at concentration levels between 10 and 20 micrograms 1(-1). The comparison with a wastewater matrix led to similar results. The enrichment procedure was applied to real samples, e.g., samples of ammunition wastewater.