Trace analysis of explosives in soil: Pressurized fluid extraction and gas and liquid chromatography-mass spectrometry

被引:22
作者
Campbell, S
Ogoshi, R
Uehara, G
Li, QX [1 ]
机构
[1] Univ Hawaii Manoa, Dept Mol Biosci & Bioengn, Honolulu, HI 96822 USA
[2] Univ Hawaii Manoa, Dept Trop Plant & Soil Sci, Honolulu, HI 96822 USA
关键词
D O I
10.1093/chromsci/41.6.284
中图分类号
Q5 [生物化学];
学科分类号
071010 [生物化学与分子生物学]; 081704 [应用化学];
摘要
Soil samples are collected from the former Open Burn/Open Detonation Unit, Makua Military Reservation, on the island of Oahu, Hawaii. The soil is the Helemano series. The soil samples are fortified with eight explosives for development of the analytical method. These analytes are 2-amino-4,6-dinitrotoluene; 1,3-dinitrobenzene; 2,4-dinitrotoluene (DNT); hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX); nitrobenzene (NB); octogen; 1,3,5-trinitrobenzene; and 2,4,6-trinitrotoluene. The analytes are recovered with pressurized fluid extraction and measured with liquid chromatography (LC), LC-mass spectrometry (MS), and gas chromatography-MS. Average recoveries of the seven analytes, except for NB, range from 67% to 110% from freshly fortified samples. The procedure fails to extract NB in soil. The average recoveries decrease from 67-110% to 41-81% as the soil is aged for 1 day to 6 months after fortification of the soil with the seven explosives. The field samples are analyzed for the presence of explosives, of which DNT and RDX are indeed detected. The results obtained with this procedure agree well with those obtained by an independent laboratory following the standard U.S. Environmental Protection Agency (EPA) method SW-846 8330. Compared with the EPA method, this new method provides MS confirmation of the analytes, and the extraction requires approximately 15 min, rather than 18 h by the EPA method.
引用
收藏
页码:284 / 288
页数:5
相关论文
共 21 条
[1]
Method for the analysis of phloxine B, uranine, and related xanthene dyes in soil using supercritical fluid extraction and high performance liquid chromatography [J].
AlcantaraLicudine, JP ;
Kawate, MK ;
Li, QX .
JOURNAL OF AGRICULTURAL AND FOOD CHEMISTRY, 1997, 45 (03) :766-773
[2]
DEGRADATION OF HEXAHYDRO-1,3,5-TRINITRO-1,3,5-TRIAZINE (RDX) BY STENOTROPHOMONAS-MALTOPHILIA PB1 [J].
BINKS, PR ;
NICKLIN, S ;
BRUCE, NC .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1995, 61 (04) :1318-1322
[3]
BOHLER A, ISEB 2001 M LEIPZ GE
[4]
In situ bioremediation of explosives-contaminated soil: A soil column study [J].
Boopathy, R ;
Widrig, DL ;
Manning, JF .
BIORESOURCE TECHNOLOGY, 1997, 59 (2-3) :169-176
[5]
Pressurized fluid extraction of nonpolar pesticides and polar herbicides using in situ derivatization [J].
David, MD ;
Campbell, S ;
Li, QX .
ANALYTICAL CHEMISTRY, 2000, 72 (15) :3665-3670
[6]
Furton KG, 2000, J FORENSIC SCI, V45, P857
[7]
Na4EDTA-assisted sub-/supercritical fluid extraction procedure for quantitative recovery of polar analytes in soil [J].
Guo, FM ;
Li, QX ;
Alcantara-Licudine, JP .
ANALYTICAL CHEMISTRY, 1999, 71 (07) :1309-1315
[8]
DETERMINATION OF THE EXPLOSIVE 2,4,6-TRINITROPHENYLMETHYLNITRAMINE (TETRYL) AND ITS TRANSFORMATION PRODUCTS IN SOIL [J].
HARVEY, SD ;
FELLOWS, RJ ;
CAMPBELL, JA ;
CATALDO, DA .
JOURNAL OF CHROMATOGRAPHY, 1992, 605 (02) :227-240
[9]
Enhanced recovery of the explosive hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) from soil: Cyclodextrin versus anionic surfactants. [J].
Hawari, J ;
Paquet, L ;
Zhou, E ;
Halasz, A ;
Zilber, B .
CHEMOSPHERE, 1996, 32 (10) :1929-1936
[10]
ISOLATION OF 3 HEXAHYDRO-1,3,5-TRINITRO-1,3,5-TRIAZINE-DEGRADING SPECIES OF THE FAMILY ENTEROBACTERIACEAE FROM NITRAMINE EXPLOSIVE-CONTAMINATED SOIL [J].
KITTS, CL ;
CUNNINGHAM, DP ;
UNKEFER, PJ .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1994, 60 (12) :4608-4611