Journal of Analytical Toxicology, Vol. 34, April 2010 Headspace In-Tube Extraction Gas Chromatography– Mass Spectrometry for the Analysis of Hydroxylic Methyl-Derivatized and Volatile Organic Compounds in Blood and Urine Ilpo Rasanen, Jenni Viinamäki, Erkki Vuori, and Ilkka Ojanperä* Department of Forensic Medicine, P.O. Box 40, Kytösuontie 11, FI-00014 University of Helsinki, Finland Abstract A novel headspace in-tube extraction gas chromatography–mass spectrometry (ITEX-GC–MS) approach was developed for broadscale analysis of low molecular weight organic compounds in blood and/or urine. One sample was analyzed following in-vial derivatization with dimethyl sulfate for ethylene glycol (EG), glycolic acid (GA), formic acid (FA), other hydroxylic compounds, and another sample for underivatized volatile organic compounds. Tenax adsorbent resin was used in the microtrap, and a porous layer, open tubular GC capillary column was used for separation. MS was operated in the full-scan mode, identification was based on the Automated Mass Spectral Deconvolution and Identification System, and quantification was based on extracted ions. The limits of quantification for EG, GA, and FA in blood were 10, 50, and 30 mg/L, respectively, and the expanded uncertainties of measurement were 20%, 16%, and 14%, respectively. The procedure allowed for the first time the inclusion of EG and GA as their methyl derivatives within a quantitative HS analysis. The ITEX method described here was more sensitive for analysis of volatile organic compounds than the corresponding static headspace analysis as demonstrated for 11 representative compounds. Introduction Ethylene glycol (EG), 1,2-ethanediol, is an industrial chemical and coolant available to the public in the form of automotive antifreeze products. The inherent toxicity of unmetabolized EG is fairly low, but life-threatening toxicity follows from its metabolites. In particular, glycolic acid (GA) is responsible for the anion gap metabolic acidosis characteristic of EG poisonings, and nephrotoxicity is thought to be due to calcium oxalate (1–4). As the estimated lethal dose of EG is only 1.4 mL/kg, both accidental and suicidal poisonings have been regularly reported (5). The importance of analyzing GA to sup* Author to whom correspondence should be addressed. port the clinical diagnosis of EG poisoning has often been emphasized (6). Methanol is another industrial, low molecular weight alcohol used in paint remover and automotive antifreeze liquids, and it causes toxic exposures via its metabolites. Methanol is also a typical component of embalming fluids. The major toxic metabolite is formic acid (FA), which causes characteristic visual defects and even blindness (7). FA may also induce deep anion gap metabolic acidosis, which frequently results in a fatal outcome (8). The lethal dose of methanol is estimated to be 1–2 mL/kg, but as little as 0.3–0.9 mL/kg may be lethal without medical treatment (9). As with EG, methanol poisoning can be accidental or imply suicidal intention. In a clinical context, the presence of a determinable FA concentration in blood has been recommended as an indication for hemodialysis when methanol poisoning is suspected (10). The wide variation in lethal dose of methanol in humans to a large extent depends on the fact that many people drink this toxic alcohol mixed with the antidote ethanol, whereas those who drink neat methanol die after ingesting much smaller amounts. The other important variable is the time elapsed between drinking and initiation of emergency treatment. Volatile organic compounds (VOC) are a diverse group of low molecular weight substances, many of which possess abuse potential. The following product groups were found to be frequently associated with volatile substance abuse (VSA) fatalities in Britain (11): gas fuels, aerosols, glues, fire extinguishers, cleaning products, anesthetic agents, and alkyl nitrites. Butane from all sources accounted for the majority (70%) of VSA deaths in 2006 (11). VOC analysis is hampered by a low prevalence of positive cases combined with the wide variety of compounds to be screened, posing a challenge for organizing an appropriate analysis service. Technical challenges in sampling and storage include possible contamination from non-glass containers and stoppers and the loss of analytes due to leaking or only partially filled containers. Static headspace (HS) gas chromatographic (GC) methods Reproduction (photocopying) of editorial content of this journal is prohibited without publisher’s permission. 113 Journal of Analytical Toxicology, Vol. 34, April 2010 are the backbone of blood ethanol analysis in the medicolegal context (12). As blood alcohol methods aim for high quantitative performance and high throughput, static HS methods with isothermal column conditions are regularly applied to this task, which results in analysis cycle times of around 5 min. However, such methods cannot be accommodated to the requirements of analyzing polar alcohols other than methanol, ethanol, propanols, and butanols, much less a wider range of VOCs. A number of GC methods are available for EG analysis. The standard method in analytical toxicology involves derivatization of the diol to form the cyclic phenylboronate ester (13–17), but this method is not suited for the simultaneous analysis of GA. Methods that are able to simultaneously determine both EG and GA include silyl derivatization prior to GC with flame ionization (FID) (18) or mass spectrometric (MS) detection (19). Derivatization to methyl glycolate has also been used prior to GC–FID analysis (20,21). FA is almost exclusively determined as a methyl formate ester by HS-GC–FID following methylation with methanol in sulfuric acid (22–25). Clearly, this procedure does not allow the simultaneous analysis of FA and methanol. VOCs are usually extracted from biological material by static HS, dynamic HS, or high concentration capacity HS techniques such as HS solid-phase microextraction (SPME) prior to GC or GC–MS analysis. A comprehensive review discusses the sample handling and analytical techniques in detail and focuses on the postmortem diagnosis of VSA (26). Interestingly, derivatization has been infrequently used for VOCs, and consequently, the hydroxylic analytes EG, GA, and FA have not been included in these assays. As shown earlier, many separate analysis methods are generally needed for low molecular weight organic compounds of toxicological relevance. The purpose of the present study is to establish a rational, cost-effective approach to cover the analysis of both hydroxylic involatile and volatile substances in blood and urine using a single analytical technique based on in-tube extraction (ITEX). ITEX is a novel, dynamic HS technique in which a microtrap filled with adsorbent material is placed between a heated HS syringe and a syringe needle while a part of the HS volume is pumped by the syringe repeatedly through the microtrap. The microtrap is then rapidly flash-heated, and the enriched analytes are released by thermal desorption into the GC injector. Unlike other, similar techniques such as solid-phase dynamic extraction, ITEX does not use a needle as a support for the adsorbent. Thermodesorption takes place using an external heater around the needle body independently of GC injector temperature. In this study, we apply ITEX-GC–MS to a broad-scale scheme of low molecular weight organic compounds in two parallel samples: one analyzed following in-vial derivatization with dimethyl sulfate (DMS) for EG, GA, FA, and other hydroxylic compounds, and another analyzed for underivatized VOCs. Tenax adsorbent resin for the microtrap and a porous layer, open tubular GC capillary column (CP-PoraPLOT Q-HT) were chosen because they allow polar compounds to be analyzed together with light hydrocarbons with low affinity for water (27). 114 The procedure allows for the first time the inclusion of EG and GA as their methyl derivatives within a quantitative HS analysis. Further, the higher sensitivity of ITEX over the corresponding static HS in VOC analysis is demonstrated with 11 representative compounds. Materials and Methods Materials EG, methyl formate, and methyl methoxy acetate were purchased from Fluka (Buchs, Switzerland); ethylene-d4 glycol (EG-d4), GA, dimethyl sulfate (DMS), and 1,2-dimethoxyethane were from Aldrich (Steinheim, Germany); glycolic-d2 acid (GA-d2) was obtained from Cambridge Isotope Laboratories (Andover, MA); FA was from Merck (Darmstadt, Germany); formic-d acid (FA-d) was from Isotec (Miamisburg, OH); and tetrabutylammonium hydrogen sulfate (TBA-HSO4) was from Riedel-de Haën (Seelze, Germany). Inhalation agents included desflurane (Suprane, Pharmacia, Stockholm, Sweden), enflurane (Efrane, Abbott, Campoverde, Italy), halothane (Trothane, ISC Chemicals, Bristol, England), isoflurane (Forene, Abbott, Queenborough, Kent, England), and sevoflurane (Sevorane, Abbott, Solna, Sweden). A qualitative mixture consisting of propane, butane, 2methylpropane, and 2-methylbutane in water was prepared from Newport butane lighter gas (Keen World Marketing, Newbury, Berkshire, England) by introducing the gas underneath the water surface. A qualitative solution of 1,1,1,2-tetrafluoroethane was prepared from Plus plasting spray (Würth, Riihimäki, Finland). All other chemicals were generally pro-analysis grade and from various suppliers. Standard solutions were prepared for each analyte separately by adding a volume corresponding to 10 mg of standard compound underneath the liquid surface into a 25-mL volumetric flask containing water or methanol and filling the bottle to the mark. All standard solutions were stored and refrigerated (4°C). Sample preparation for hydroxylic organic compounds by in-vial methylation (ITEX 1) The internal standard solutions (IS-1) contained 20 mg/mL each of EG-d4, GA-d2, and FA-d in water. Urine samples Urine (0.5 mL) was measured into a 20-mL HS vial; 25 µL of IS-1 solution was added, and the sample was mixed. For standard samples, the total volume of the standard solution and urine was 0.5 mL. Anhydrous sodium sulfate (250 mg) was mixed into the solution to obtain a salting-out effect, followed by adding 50 µL of 5 M sodium hydroxide solution, 50 µL of 0.1 M TBA-HSO4, and 150 µL of DMS. The vial was closed and mixed. Blood samples Blood (0.5 g) was measured into a 10-mL test tube, 25 µL of IS-1 solution was added, and the sample was mixed. For preparing standard samples, 0.5 g of bovine blood was used and Journal of Analytical Toxicology, Vol. 34, April 2010 the corresponding standard solutions were added into the vial before the IS-1 solution. Acetonitrile (1.5 mL) was gradually added while simultaneously mixing the sample in a vortex mixer. The sample was mixed for an additional 1 min and centrifuged. The top layer was transferred into another 10-mL test tube, and the acetonitrile was evaporated under a gentle Sample preparation for volatile organic compounds without derivatization (ITEX 2) Table I. Static Headspace and In-Tube Extraction Method Parameters Parameter Incubation temperature Incubation time Agitator speed Syringe temperature Extraction volume Extraction strokes Extraction speed Desorption temperature Desorption speed Injection volume Needle flush time Trap cleaning temperature Fill speed Pull-up delay Injection speed Pre inject delay Flush time HS ITEX1* ITEX2† 60°C 300 s 500 rpm 55ºC 90°C 300 s 500 rpm 55ºC 1500 µL 10 150 µL/s 230°C 20 µL/s 2000 µL 600 s 230°C 60°C 300 s 500 rpm 55ºC 1500 µL 30 150 µL/s 230°C 20 µL/s 2000 µL 600 s 230°C 2000 µL stream of nitrogen at 40°C. The residue of approximately 250 µL was transferred into a 20-mL HS vial, and 125 mg of anhydrous sodium sulfate was mixed into the solution for saltingout. Thereafter, 50 µL of 5 M sodium hydroxide solution, 50 µL of 0.1 M TBA-HSO4, and 50 µL of DMS were added, and the vial was closed and mixed. The internal standard solution (IS-2) contained 5.0 µg/mL of diethylketone in water. Blood (1.0 g) was measured into a 20mL HS vial, and 1.0 mL of IS-2 solution was added. The vial was closed and mixed. For preparing standard samples, 1.0 g of bovine blood was used, and the corresponding standard solutions were added into the vial before the IS-2 solution. Static HS sample preparation for VOCs without derivatization was the same as described previously for ITEX2. ITEX-GC–MS The ITEX1 and ITEX2 methods used the same hardware configuration. In the static HS method, the ITEX injection unit was replaced with a standard HS unit. ITEX2 parameters were optimized to obtain high sensitivity for VOCs. The same parameters were used in ITEX1 if applicable, but the derivatization procedure for EG, GA, and FA required a higher incubation temperature, and the required sensitivity was obtained with fewer extraction strokes. Final ITEX1, ITEX2, and static HS method parameters are shown in Table I. GC–MS was performed with a 5975B VL mass selective detector coupled with a 6890N GC from Agilent Technologies (Santa Clara, CA). The GC was equipped with a CTC Analytics 100 µL/s 1000 ms 20 µL/s 500 ms 10 s * Ethylene glycol, glycolic acid, formic acid, and polar organic compounds. † Volatile organic compounds. Table II. Validation Data for Ethylene Glycol, Glycolic Acid, and Formic Acid in Blood and Urine Blood Target Ion* (m/z) Q1* (m/z) Q2* (m/z) Ethylene-d4 glycol-2ME 94 64 47 Ethylene glycol-2ME 90 60 45 Glycolic-d2 acid-2ME 76 47 Glycolic acid-2ME 74 45 Formic-d acid-ME 61 32 Formic acid-ME# 60 31 Derivative Linear range (mg/L) R2 LOD† (mg/L) S/N‡ Urine LOQ (mg/L) S/N U95§ (%) Linear range (mg/L) R2 LOD (mg/L) LOQ S/N (mg/L) S/N U95 (%) 10–20,000 0.9996 3 6 10 23 20 30–20,000 0.996 10 4 30 29 13 50–20,000 0.997 10 9 50 28 16 50–20,000 0.996 30 10 50 14 12 30 699 14 50–5000 0.9989 50 595 14 30–4000 0.9991 * Extracted target ions and qualifier ions (Q) of methyl derivatives used for quantification in full-scan gas chromatography–mass spectrometry. † LOD = lower limit of detection; LOQ = lower limit of quantification. ‡ Signal-to-noise ratio at LOD or LOQ. § Expanded uncertainty of measurement corresponding to 95% confidence. # LOD was not determined because of endogenous FA. 115 Journal of Analytical Toxicology, Vol. 34, April 2010 CombiPal autosampler with ITEX and static HS options (Zwingen, Switzerland). The column was a CP-PoraPLOT Q-HT capillary column from Varian (25 m × 0.32-mm i.d., 10-µm film thickness, and 2.5-m particle trap, Lake Forest, CA). A 2.5-mL HS syringe was used (Hamilton, Bonaduz, Switzerland). In the ITEX methods, a microtrap containing 44 mg of Tenax TA 80/100 mesh from Supelco (Bellefonte, PA) was attached to the syringe needle. The GC–MS was operated with ChemStation software (Agilent) with integrated CTC Control software. Qualitative data analysis was performed using AMDIS software. The GC was used in the splitless mode with a constant column flow of 2 mL/min. The injector port temperature was 200°C, and the transfer line temperature was 280°C. The oven temperature was initially kept at 40°C for 2 min and then increased by 15°C/min to 250°C, which was kept for 4 min (ITEX1) or 10 min (ITEX2). The mass detector was operated in electron-ionization and full-scan mode in the range m/z 15– 550. For the analysis of EG, GA, and FA methyl derivatives, target and qualifier ions were selected from the full-scan data (Table II), and quantification was performed using these extracted ions. Validation of quantification In the validation of the ITEX1 method, the following parameters were evaluated: selectivity (analysis of blank and spiked matrix samples), linearity, accuracy (bias), precision (spiked and real samples), repeatability (duplicate analysis on two different days; sample preparation performed by different persons), lower A B limit of detection (LOD), and lower limit of quantification (LOQ). Five parallel spiked samples in 15 levels were prepared in the concentration range of 5 mg/L to 20 g/L. The criteria for the LOQ and linear range were ± 20% relative standard deviation (RSD) in precision, bias within ± 20% of the reference value, and signal-to-noise ratio (S/N) of > 10. The criterion for LOD was S/N > 3. The estimation of uncertainty of measurement (U) was based on the EURACHEM approach (28), using data described earlier. U was reported as the expanded uncertainty of measurement corresponding to 95% confidence according to the following equation: U95 = 2(U12 + U22)½, where U1 is the systematic error (mean accuracy from calibration and proficiency test samples) and U2 is the random error (mean precision and reFigure 1. Analysis scheme for low molecular weight hydroxylic organic compounds in blood and urine peatability from calibration and real (ITEX1) (A) and for volatile organic compounds in blood (ITEX2) (B). NIST MS or other library search was samples). performed only when required. AMDIS Figure 2. In-vial methylation of ethylene glycol (EG), glycolic acid (GA), and formic acid (FA) with dimethyl sulfate producing EG-2ME, GA-2ME, and FA-ME, respectively. 116 AMDIS is a computer program that extracts spectra for individual components in a GC–MS data file and identifies target compounds by matching the spectra against a reference library. The software was developed at the U.S. National Institute of Standards and Technology (NIST) and is freely available (http://chemdata. nist.gov/mass-spc/amdis/). AMDIS is included in the NIST/EPA/NIH mass spectral library and also includes Lib2NIST converter software, which can be used to convert ChemStation libraries to AMDIS libraries. In the present study, the AMDIS search was performed with an in-house target library containing spectra of underivatized compounds and the corresponding methyl esters or ethers. For the calculation of AMDIS match factors, the correlation between extracted spectrum and library spectrum was utilized. An NIST MS search or a manual search against other libraries was performed for unidentified peaks when necessary. Journal of Analytical Toxicology, Vol. 34, April 2010 Results and Discussion EG, GA, FA, and hydroxylic organic compounds Figure 1 shows the analysis scheme for low molecular weight hydroxylic organic compounds in blood and urine (ITEX1) and for VOCs in blood (ITEX2). Different sample preparation procedures were applied in these two methods, while the GC–MS analysis was the same, except for the isothermal time kept at the final oven temperature. Hydroxylic and carboxylic compounds in biological material could be readily derivatized by in-vial methylation with DMS to form ethers and esters, respectively, making EG, GA, and FA amenable to HS analysis (Figure 2). The GC retention times of hydroxylic organic compounds, as their methyl derivatives (ITEX1) and underivatized VOCs (ITEX2), are shown in Table III. Many glycols, alcohols, phenol as well as γ-hydroxybutyric acid could be detected by the method. The boiling points of the compounds and derivatives included were generally below 160°C. Methanol could not be included as an analyte in ITEX1 as the decomposition of the DMS reagent produces Table III. Gas Chromatographic Retention Times (RT) on a Porous Layer, Open Tubular Column* for Low Molecular Weight Hydroxylic Organic Compounds as Their Methyl Derivatives (ITEX1) and Underivatized Volatile Organic Compounds (ITEX2) Compound 1,1,1,2-Tetrafluoroethane Propane Methanol Acetaldehyde Formic-d acid Formic acid (FA) Methyl formate Isobutane Desflurane Ethanol Butane Acetonitrile Acetone Isopropyl alcohol Methylene chloride Sevoflurane Carbon disulfide 2-Methylbutane Diethyl ether Dimethoxymethane Isoflurane 1-Propanol Pentane Enflurane tert-Butanol 2-Methylpropanal Halothane Ethylmethyl ketone Butanal Chloroform Ethyl acetate Tetrahydrofuran Methyl-tert-butyl ether (MTBE) 2-Butanol Methyl propionate 2-Methyl-1-propanol 1,2-Dichloroethane Hexane 1-Butanol RT (min) ITEX1† RT (min) ITEX2‡ 8.4 9.5 9.5 10.9 11.7 11.8 16.0 16.4 16.2 16.8 11.8 11.9 12.3 12.3 12.4 13.0 13.7 13.9 14.0 14.3 14.5 14.5 14.5 14.5 14.6 14.6 14.7 14.9 15.2 15.4 15.7 15.8 15.8 16.0 16.0 16.0 16.1 16.1 16.2 16.3 16.6 16.7 16.8 Compound Ethylene-d4 glycol Ethylene glycol (EG) 1,1,1-Trichloroethane Di-isopropyl ether Benzene Carbon tetrachloride Ethyl-tert-butyl ether (ETBE) Cyclohexane Trichloroethylene 3-Methylbutanal Diethyl ketone Pentanal Ethyl propionate 2-Pentanol tert-Amyl methyl ether (TAME) 1,2-Propanediol Triethylamine Glycolic-d2 acid Glycolic acid (GA) 2,3-Butanediol Heptane Pyridine 1,3-Propanediol Isopentyl alcohol 1-Pentanol Methyl isobutyl ketone Toluene Tetrachloroethylene Hexanal Butyl acetate 1,2-Butanediol 1,3-Butanediol 1,4-Butanediol m-Xylene p-Xylene o-Xylene Phenol 1,1,1,2-Tetrachloroethane γ-Hydroxybutyric acid (GHB) RT (min) ITEX1† RT (min) ITEX2‡ 16.9 16.9 18.3 17.0 17.1 17.2 17.2 17.2 17.4 17.4 17.4 17.7 17.9 17.9 18.0 18.1 18.2 18.5 18.5 18.5 18.6 18.7 18.7 18.9 18.8 18.9 19.0 19.0 19.4 19.6 20.0 20.4 20.5 20.5 20.8 21.9 22.9 22.9 23.0 23.7 23.8 24.7 * CP-PoraPLOT Q-HT capillary column (25 m × 0.32-mm i.d., 10-µm film thickness, 2.5-m particle trap). † Retention time for methyl derivative. ‡ Retention times sorted according to ITEX2. 117 Journal of Analytical Toxicology, Vol. 34, April 2010 methanol and sulfuric acid. However, methanol was readily desilylation (34). However, the methylation reaction with DMS tected with ITEX2. In ITEX1, some dimethoxy methane was appears to be the method of choice where direct derivatization detected in all samples and reagent blanks, probably forming in an aqueous sample is an option. DMS has been recently from methanol. Putrefied samples, especially urine samples, used in several in situ derivatization applications for organic showed a higher background than usual, but this was effiacids in water (35–38) or urine samples (39) prior to GC–MS ciently compensated for by the use of deuterated internal analysis with HS (35), HS-SPME (36,38,39), or large-volume standards. FA was found in many postmortem samples at on-column injection (37). The methylation procedure used in approximately 50 mg/L, possibly due to postmortem changes. this study is a modification of these previously presented The validation data for EG, GA, and FA are shown in Table methods. The reaction mixture consisted of DMS as the methyII. All three analytes possessed good linearity over the toxicolation agent, the catalyzing ion-pairing agent TBA-HSO4, sodium sulfate to improve the salting-out effect by increasing logically relevant concentration range. The expanded uncerthe ionic strength, and sodium hydroxide for adjusting the tainty of measurement (level of confidence 95%) was no pH. The toxicity of DMS warrants appropriate precautions in higher than 20%. Comparison to previous studies indicates sample work-up and waste disposal. that, for EG and GA, the present values of LOD and LOQ in blood, which range from 3 to 50 mg/L, are similar to the VOC values obtained with GC–FID or GC–MS (4 to 25 mg/L) folThe ITEX2 method allowed the qualitative analysis of a comlowing derivatization with phenyl boronic acid or silylation prehensive range of VOCs in blood without sample work-up reagents (29). As the plasma EG concentration of 200 mg/L other than the addition of an internal standard. Table III lists has been considered the threshold of toxicity for systemic exposure (19,30) and plasma GA concentrations of 980 mg/L or higher have been associated with renal injury (30), the present method clearly meets the sensitivity and quantification range requirements. In the treatment of EG poisoning, hemodialysis has traditionally been indicated for patients with a serum EG concentration greater than 500 mg/L (4), but there are no established action limits for GA (31). Very low LOD and LOQ have been reported for EG and GA using direct injection GC–MS following derivatization with bis-N,O-trimethylsilyl trifluoroacetamide (32), but according to those Figure 3. ITEX1-GC–MS total ion chromatogram from a postmortem blood sample related to a fatal authors, the values obtained are far poisoning case due to ingestion of EG. Peak identification: 1, FA-d-ME; 2, acetonitrile; 3, EG-d4-2ME below the limits seen in patient intoxiand EG-2ME; and 4, GA-d2-2ME and GA-2ME. The concentrations of EG and GA in blood were 1.4 and cation. 2.1 g/L, respectively. For FA, the LOQ obtained in blood was 30 mg/L (Table II). This value is lower than the LOQ of 100 mg/L reported with GC–FID following Table IV. Comparison of Identification Limits* for VOCs derivatization with methanol in sulfuric acid (24,25). FA conin Blood by ITEX2 and Static HS Methods centrations in postmortem blood between 600 and 1400 mg/L have been found in 97% of 74 fatal methanol poisoning cases. ITEX2 HS Compound (µg/L) (µg/L) Unlike methanol concentrations alone, FA concentrations have been highly correlated with fatal outcome (24). In a clinical Acetone† 0.9 100 context, serum methanol concentration over 500 mg/L is an inDesflurane 0.5 70 dication for hemodialysis (33), but there are no established acEnflurane 3 20 tion limits for FA (31). Ethanol 15,000 120,000 Figure 3 shows an ITEX1-GC–MS total ion chromatogram Ethyl acetate 5 30 from a postmortem blood sample related to a fatal poisoning Diethyl ether 1 100 case due to ingestion of EG. The concentrations of EG and GA Hexane 0.5 7 in blood were 1.4 and 2.1 g/L, respectively, and in urine were Methanol 100 80,000 3.4 and 4.2 g/L, respectively. MTBE 5 40 In-vial derivatization applied directly to the biological maSevoflurane 5 40 Toluene 2 20 terial is a key step in terms of ease of use and speed of the ITEX1 method for hydroxylic organic compounds. In GC anal* Minimum required AMDIS spectral match factor set to 80 (maximum 100). ysis, numerous derivatization methods are available for hy† Determined in a water sample because of endogenous acetone present in blood. droxyl groups, such as acylation, alkylation, esterification, and 118 Journal of Analytical Toxicology, Vol. 34, April 2010 the retention times for 62 VOCs of toxicological relevance, intimes, independence from GC injector temperature and, imcluding the gas fuel components propane, butane, 2-methylportantly, lower LODs (40). Compared with a purge and trap propane, and 2-methylbutane. A spectral library was created by GC–MS method (41), higher LODs were obtained, but a benefit ChemStation software and, after adding retention times in of ITEX was a much shorter analysis cycle time. seconds and CAS numbers, the library was converted to AMDIS The identification limits obtained here for VOCs compared library by the Lib2NIST converter. ITEX2 method was favorably with those reported in the literature for blood using amenable to semiquantitative analysis using diethyl ketone as various extraction and analysis techniques (26,42). The ITEX2 an internal standard. However, for precise quantification, inmethod appears to be sensitive enough to reveal occupational dividually selected internal standards should be used. exposure well below acutely toxic levels. This is exemplified AMDIS software proved to be an indispensable tool for recwith the workers exposed to toluene at low levels during proognizing target analytes in the full-scan GC–MS acquisition duction of adhesive tapes, who exhibited a mean blood toluene data. The program analyzes individual single ion chroconcentration of 18 µg/L (43). Another example relates to the matograms to automatically identify possible component peaks exposure to the common gasoline oxygenate methyl tert-butyl within a data set. All masses that have the same chromatoether (MTBE) during tank truck loading. The fuel loaders were graphic characteristics are then put forward as the unknown found to have MTBE levels in blood averaging 13 and 19 µg/L spectrum for a spectral search within a selected target library. at colder and warmer ambient temperature, respectively (44). The overall process involves four sequential steps: noise analysis, component perception, spectral deconvolution, and compound identification. Conclusions Identification limits of 11 VOCs based on AMDIS spectral match were compared between ITEX2 and the corresponding The ITEX1-GC–MS procedure is a viable method for the static HS method. Default parameters were used with AMDIS screening or quantitative confirmation of suspected EG poiwith the minimum required spectral match factor set to 80 sonings and for the confirmation of methanol findings from a (maximum 100). Table IV shows that ITEX2 was superior to the standard HS blood alcohol analysis. Delayed sampling folcorresponding static HS with all compounds tested. The GC lowing ingestion of a toxic alcohol may result in undetectable peak shape was generally good, but further improvement in the EG or methanol but still measurable GA or FA in biological analysis of some very volatile and early eluting compounds could probably be obtained by cryofocusing. The fairly high identification limit of ethanol compared to methanol was mainly due to a non-optimal chromatographic peak shape of ethanol. Figure 4 shows an ITEX2-GC–MS analysis of a postmortem blood sample related to a case of fatal poisoning due to inhalation of butane. The main findings, as verified from mass spectra and retention times, were butane, isobutane, and propane. As ITEX is a new microextraction technique, not much literature on its applications is currently available. A recent, thorough study reported the optimization and evaluation of a fully automated ITEX method for the enrichment of volatile organic hydrocarbons from aqueous samples prior to GC–MS analysis (40). The technique was found to be comparable to other in-needle extraction techniques in terms of the governing parameters for method optimization. These include extraction temperature, the number of extraction cycles, extraction flow rate and volume, and desorpFigure 4. ITEX2-GC–MS total ion chromatogram and the corresponding mass spectra from a postmortem tion flow rate and volume. The advanblood sample related to a fatal poisoning case due to inhalation of butane. Findings: propane (peak 1, tages provided by ITEX over the spectrum A), isobutane (peak 2, spectrum B), butane (peak 3, spectrum C), and internal standard diethyl commonly used HS-SPME were lower ketone (peak 4). fragility, longer extraction phase life- 119 Journal of Analytical Toxicology, Vol. 34, April 2010 fluids. The present approach is the first practical HS method for the quantitative analysis of EG, GA, and FA in biological material. The ITEX2-GC–MS allows screening for a wide range of VOCs to reveal exposure to fuel gases, gasoline, alcohols, solvents, glues, anesthetic agents, and organic nitrites. The procedure has a sufficiently high performance to disclose the majority of harmful agents in blood at subtoxic concentrations. As findings of EG, methanol, and VOCs are rather infrequent, the shared analytical set-up used for ITEX1 and ITEX2 is advantageous in utilizing the sophisticated instrumentation in a costeffective manner. Because of the full-scan MS data acquisition and AMDIS capabilities, the current procedure can be extended to analyze any other low molecular weight compound that is sufficiently volatile or can be volatilized by methylation. References 1. K.L. Clay and R.C. Murphy. On the metabolic acidosis of ethylene glycol intoxication. Toxicol. Appl. Pharmacol. 39: 39–49 (1977). 2. D. Jacobsen, N. Ostby, and J.E. Bredesen. Studies on ethylene glycol poisoning. Acta Med. Scand. 212: 11–15 (1982). 3. D. Jacobsen, S. Ovrebø, J. Ostborg, and O.M. Sejersted. Glycolate causes the acidosis in ethylene glycol poisoning and is effectively removed by hemodialysis. Acta Med. Scand. 216: 409–416 (1984). 4. J. Brent. Current management of ethylene glycol poisoning. Drugs 61: 979–988 (2001). 5. P.M. Leth and M. Gregersen. Ethylene glycol poisoning. Forensic Sci. Int. 155: 179–184 (2005). 6. A.D. Fraser. Importance of glycolic acid analysis in ethylene glycol poisoning. Clin. Chem. 44: 1769–1770 (1998). 7. G. Martin-Amat, K.E. McMartin, S.S. Hayreh, M.S. Hayreh, and T.R. Tephly. Methanol poisoning: ocular toxicity produced by formate. Toxicol. Appl. Pharmacol. 45: 201–208 (1978). 8. D. Jacobsen and K.E. McMartin. Antidotes for methanol and ethylene glycol poisoning. J. Toxicol. Clin. Toxicol. 35: 127–143 (1997). 9. The International Programme on Chemical Safety (IPCS). Environmental Health Criteria 196. http://www.inchem.org/documents/ehc/ehc/ehc196.htm. Accessed July 2009. 10. J.D. Osterloh, S.M. Pond, S. Grady, and C.E. Becker. Serum formate concentrations in methanol intoxication as a criterion for hemodialysis. Ann. Intern. Med. 104: 200–203 (1986). 11. M.E. Field-Smith, B.K. Butland, J.D. Ramsey, and H.R. Anderson. Report 21: Trends in death associated with abuse of volatile substances 1971–2006, July 2008. St. George’s University of London, London, U.K. http://www.vsareport.org. Accessed July 2009. 12. A.W. Jones and J. Schuberth. Computer-aided headspace gas chromatography applied to blood-alcohol analysis: importance of online process control. J. Forensic Sci. 34: 1116–1127 (1989). 13. W.H. Porter and A. Auansakul. Gas-chromatographic determination of ethylene glycol in serum. Clin. Chem. 28: 75–78 (1982). 14. R.J. Flanagan, S. Dawling, and B.M. Buckley. Measurement of ethylene glycol (ethane-1,2-diol) in biological specimens using derivatisation and gas-liquid chromatography with flame ionisation detection. Ann. Clin. Biochem. 24: 80–84 (1987). 15. N.B. Smith. Identification and elimination of an ethylene glycol determination artifact. Clin. Chim. Acta 162: 105–108 (1987). 16. P. Houzé, J. Chaussard, P. Harry, and M. Pays. Simultaneous determination of ethylene glycol, propylene glycol, 1,3-butylene glycol and 2,3-butylene glycol in human serum and urine by wide-bore column gas chromatography. J. Chromatogr. 619: 251– 257 (1993). 17. W.H. Porter, M.C. Jarrells, and D.H. Sun. Improved specificity for ethylene glycol determined as the phenylboronate by capillary column gas chromatography. Clin. Chem. 40: 850–851 (1994). 120 18. H.H. Yao and W.H. Porter. Simultaneous determination of ethylene glycol and its major toxic metabolite, glycolic acid, in serum by gas chromatography. Clin. Chem. 42: 292–297 (1996). 19. W.H. Porter, P.W. Rutter, and H.H. Yao. Simultaneous determination of ethylene glycol and glycolic acid in serum by gas chromatography–mass spectrometry. J. Anal Toxicol. 23: 591–597 (1999). 20. A.D. Fraser and W. MacNeil. Colorimetric and gas chromatographic procedures for glycolic acid in serum: the major toxic metabolite of ethylene glycol. J. Toxicol. Clin. Toxicol. 31: 397–405 (1993). 21. C.L. Moreau, W. Kerns, II, C.A. Tomaszewski, K.E. McMartin, S.R. Rose, M.D. Ford, and J. Brent. Glycolate kinetics and hemodialysis clearance in ethylene glycol poisoning. META Study Group. J. Toxicol. Clin. Toxicol. 36: 659–666 (1998). 22. C. Abolin, J.D. McRae, T.N. Tozer, and S. Takki. Gas chromatographic head-space assay of formic acid as methyl formate in biologic fluids: potential application to methanol poisoning. Biochem. Med. 23: 209–218 (1980). 23. A.D. Fraser and W. MacNeil. Gas chromatographic analysis of methyl formate and application in methanol poisoning cases. J. Anal. Toxicol. 13: 73–76 (1989). 24. G.R. Jones, P.P. Singer, and K. Rittenbach. The relationship of methanol and formate concentrations in fatalities where methanol is detected. J. Forensic Sci. 52: 1376–1382 (2007). 25. H.R. Wallage and J.H. Watterson. Formic acid and methanol concentrations in death investigations. J. Anal. Toxicol. 32: 241– 247 (2008). 26. S.M. Wille and W.E. Lambert. Volatile substance abuse—postmortem diagnosis. Forensic Sci. Int. 142: 135–156 (2004). 27. I. Ojanperä, K. Pihlainen, and E. Vuori. Identification limits for volatile organic compounds in the blood by purge-and-trap GC–FTIR. J. Anal. Toxicol. 22: 290–295 (1998). 28. EURACHEM/CITAC Guide GC4: Quantifying Uncertainty in Analytical Measurement, 2nd ed, S.L.R. Ellison, M. Rosslein, and A. Williams, Eds. EURACHEM/CITAC, 2000, http://www. measurementuncertainty.org/index.html (October 2009). 29. R. Hess, M.J. Bartels, and L.H. Pottenger. Ethylene glycol: an estimate of tolerable levels of exposure based on a review of animal and human data. Arch. Toxicol. 78: 671–680 (2004). 30. J. Brent, K. McMartin, S. Phillips, K.K. Burkhart, J.W. Donovan, M. Wells, and K. Kulig. Fomepizole for the treatment of ethylene glycol poisoning. N. Engl. J. Med. 340: 832–838 (1999). 31. A.D. Fraser, L. Coffin, and D. Worth. Drug and chemical metabolites in clinical toxicology investigations: the importance of ethylene glycol, methanol and cannabinoid metabolite analyses. Clin. Biochem. 35: 501–511 (2002). 32. P. van Hee, H. Neels, M. de Doncker, N. Vrydags, K. Schatteman, W. Uyttenbroeck, N. Hamers, D. Himpe, and W. Lambert. Analysis of gamma-hydroxybutyric acid, DL-lactic acid, glycolic acid, ethylene glycol and other glycols in body fluids by a direct injection gas chromatography–mass spectrometry assay for wide use. Clin. Chem. Lab. Med. 42: 1341–1345 (2004). 33. D.G. Barceloux, G.R. Bond, E.P. Krenzelok, H. Cooper, and J.A. Vale. American Academy of Clinical Toxicology Ad Hoc Committee on the Treatment Guidelines for Methanol Poisoning. American Academy of Clinical Toxicology practice guidelines on the treatment of methanol poisoning. J. Toxicol. Clin. Toxicol. 40: 415–446 (2002). 34. M. Rompa, E. Kremer, and B. Zygmunt. Derivatisation in gas chromatographic determination of acidic herbicides in aqueous environmental samples. Anal. Bioanal. Chem. 377: 590–599 (2003). 35. P.L. Neitzel, W. Walther, and W. Nestler. In situ methylation of strongly polar organic acids in natural waters supported by ionpairing agents for headspace GC–MSD analysis. Fresenius J. Anal. Chem. 361: 318–323 (1998). 36. M.N. Sarrion, F.J. Santos, and M.T. Galceran. In situ derivatization/solid-phase microextraction for the determination of haloacetic acids in water. Anal. Chem. 72: 4865–4873 (2000). Journal of Analytical Toxicology, Vol. 34, April 2010 37. M.I. Catalina, J. Dallüge, R.J.J. Vreuls, and U.A.T. Brinkman. Determination of chlorophenoxy acid herbicides in water by in situ esterification followed by in-vial liquid-liquid extraction combined with large-volume on-column injection and gas chromatography–mass spectrometry. J. Chromatogr. A 877: 153–166 (2000). 38. L. Araujo, J. Wild, N. Villa, N. Camargo, D. Cubillan, and A. Prieto. Determination of anti-inflammatory drugs in water samples, by in situ derivatization, solid phase microextraction and gas chromatography–mass spectrometry. Talanta 75: 111–115 (2008). 39. N. Li, C. Deng, and X. Zhang. Determination of methylmalonic acid and glutaric acid in urine by aqueous-phase derivatization followed by headspace solid-phase microextraction and gas chromatography–mass spectrometry. J. Sep. Sci. 30: 266–271 (2007). 40. M.A. Jochmann, X. Yuan, B. Schilling, and T.C. Schmidt. In-tube extraction for enrichment of volatile organic hydrocarbons from aqueous samples. J. Chromatogr. A 1179: 96–105 (2008). 41. E. Martínez, S. Lacorte, I. Llobet, P. Viana, and D. Barceló. Multicomponent analysis of volatile organic compounds in water by automated purge and trap coupled to gas chromatography–mass spectrometry. J. Chromatogr. A 959: 181–190 (2002). 42. F. Pragst. Application of solid-phase microextraction in analytical toxicology. Anal. Bioanal. Chem. 388: 1393–1414 (2007). 43. T. Kawai, H. Ukai, O. Inoue, Y. Maejima, Y. Fukui, F. Ohashi, S. Okamoto, S. Takada, H. Sakurai, and M. Ikeda. Evaluation of biomarkers of occupational exposure to toluene at low levels. Int. Arch. Occup. Environ. Health 81: 253–262 (2008). 44. S. Vainiotalo, K. Pekari, and A. Aitio. Exposure to methyl tert-butyl ether and tert-amyl methyl ether from gasoline during tank lorry loading and its measurement using biological monitoring. Int. Arch. Occup. Environ. Health 71: 391–396 (1998). Manuscript received August 21, 2009; revision received November 4, 2009. 121
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