AN ABSTRACT OF THE THESIS OF Yan Hu for the degree of Master in Science in Chemistry presented on June 19, 2009. Title: Determination of Ethyl Glucuronide and Ethyl Sulfate as Human Biomarkers of Alcohol Exposure in Urine by Liquid Chromatography/Electrospray Tandem Mass Spectrometry with Large Volume Injection Abstract approved: _____________________________________________________________________ Jennifer A. Field Staci L. Simonich This research was undertaken to develop a sensitive, selective, and rapid analytical method to measure ethyl glucuronide (EtG) and ethyl sulfate (EtS) in urine as urinary biomarkers of alcohol exposure. Large-volume injection (LVI) coupled with liquid chromatography / electrospray tandem mass spectrometry was used to eliminate the need for either off-line or on-line solid phase extraction. Urine sample preparation was limited to diluting the urine 1:1000 with deionized water prior to large-volume injection (900 μL). Three MS/MS transitions were monitored for EtG and two MS/MS transitions were monitored for EtS, with the deprotonated molecular ion [M-H]- as the precursor ion: m/z 221→75, 221→85, 221→113(EtG) and 125→80, 125→97(EtS). Pentadeuterated EtG and pentadeuterated EtS were used as internal standards for EtG and EtS, respectively. The method was accurate with recoveries from 99.8% to 102.9% for EtG and 93.3% to 102.5% for EtS and gave good precision, as indicated by average RSD, of 3.5% and 4.9% for EtG and EtS, respectively. Matrix effects were eliminated and the instrumental detection limit was 0.005 μg/mL for EtG and 0.010 μg/mL for EtS, which is a factor of 10 lower than previous published analytical methods for measuring EtG and EtS. The method quantification limits were 0.015 μg/mL for EtG and 0.025 μg/mL for EtS in 1:1000 diluted urine, corresponding to 15 μg/mL for EtG and 25 μg/mL for EtS in undiluted urine. Finally, the developed method gave statistically equivalent results when applied to measuring EtG and EtS in a third-party reference urine. ©Copyright by Yan Hu June 19, 2009 All Rights Reserved Determination of Ethyl Glucuronide and Ethyl Sulfate as Human Biomarkers of Alcohol Exposure in Urine by Liquid Chromatography/Electrospray Tandem Mass Spectrometry with Large Volume Injection by Yan Hu A THESIS Submitted to Oregon State University in partial fulfillment of the requirements for the degree of Master of Science Presented June 19, 2009 Commencement June 2010 Master of Science thesis of Yan Hu presented on June 19, 2009. APPROVED: Co-major Professor, representing Chemistry Co-major Professor, representing Chemistry Chair of the Department of Chemistry Dean of the Graduate School I understand that my thesis will become part of the permanent collection of Oregon State University libraries. My signature below authorizes release of my thesis to any reader upon request. Yan Hu, Author ACKNOWLEDGEMENTS I would like to give special thanks to my advisors Dr. Staci Simonich and Dr. Jennifer Field for their guidance, support and input throughout the course of my studies. Many thanks to my academic committee: Dr. Claudia Maier, and Dr. Fredrick Prahl, for their advice on the dissertation content throughout the committee meetings and examinations. Thanks also to Aurea Chiaia, Dr. Jeff Moore and the Simonich lab for their expertise. Thanks to the faculty and staff of the Department of Chemistry and Department of Environmental and Toxicology who directly or indirectly contribute to my work. Warmly thanks to my friends for their support and good times. Finally, I would like to thank my parents for all their love, support and encouragement throughout the development of my thesis. TABLE OF CONTENTS Page 1 Introduction……………………………………………………………………..1 2 Experimental …………………………………………………………………...11 2.1 Standards and Reagents………………………………….………………..11 2.2 Preparation of Stock and Working Solutions………….…...…………....12 2.3 Sample Preparation………………………………………..………...….....13 2.4 Instrumentation…………………………………………….………….…..14 2.4.1 High Pressure Liquid Chromatography (HPLC)………….….………14 2.4.2 Electrospray Tandem Mass Spectrometry(ESI-MS/MS)……...…......14 3 2.5 Injection Volume and Dilution Factor Optimization…...……………........19 2.6 Specificity…………………………………………………………………20 2.7 Stability…………………………………………………………………...20 2.8 Matrix effects…………………………………………...…………………21 2.9 Validation ………………………………………………………………...21 Results and Discussion ………………………………………………………22 3.1 Method Development…………………………………………..…………22 3.1.1 Chromatography………………………………………………….…..23 3.1.2 Optimization of Mobile Phase……………………………………..…25 3.1.3 Optimization of Injection Volume……………………….…………..28 3.1.4 Optimization of Sample Dilution Factor………………….........….29 TABLE OF CONTENTS (Continued) Page 3.2 Method Validation…………………………………………………...……30 3.2.1 Specificity………………………………………………………….…30 3.2.2 Linearity………………………………………………………...……32 3.2.3 Matrix Effects……………………………………………….……….34 3.2.4 Accuracy and Precision……………………………………………..36 3.2.5 Detection and Quantification Limits…………………………………39 3.3 Method Verification………………………..…………………......………39 4 Conclusions………………………………………………………...……………41 5 Acknowledgements…………………………………………………………...…42 6 References…………………………………………………………………...…..43 LIST OF FIGURES Figures Page 1. Elimination pathways for ethanol in the human body, showing the major, oxidate route, and the minor conjugation reactions with sulfate and glucuronic acid……………………………………………………….....……..…..2 2. Chemical structures and molecular formulas of EtG and EtS and pentadeuterated internal standards……………………………………………………....4 3. Product-ion spectra of EtG and EtG-D5…………………………………………18 4. Product-ion spectra of EtS and EtS-D5 ……….………………………………...18 5. Modified injection of an Agilent 1100 HPLC with the locations of the 1400 μL stainless steel seat extension loop and seat capillary indicated………………….19 6. Chromatograms of EtG (0.08 μg/mL), EtG-D5, EtS(0.08 μg/mL) and EtS-D5 in a spiked urine sample with a 900 μL injection volume with MRM transitions ………………………………………………………………………..24 7. Chromatograms of EtG and EtS spiked into 1:1000 diluted blank urine and separated with different ammonium acetate concentration in the 0.1% formic acid mobile phase including: (A) 5 mM ammonium acetate, (B) 10 mM ammonium acetate, (C) 15 mM ammonium acetate, and (D) 30 mM ammonium acetate....…………………………………………………………………...….....27 8. MRM chromatograms of EtG, EtS, EtG-d5 and EtS-D5 in blank urine (A, C, E and G) and spiked blank urine (diluted 1:1000) with a final concentration of 0.05 μg/mLfor each analyte (B, D, F and H) ……………….…………………….…..31 9. Representative calibration curves in deionized water and 1:1000 dilute blank urine for EtG and EtS ……..........................................................…..………...….33 10. LC-ESI-MS/MS chromatograms in urine sample. (A) dilute reference certified urine containing 0.050μg/mL EtG and EtS, and (B) blank urine that was not spiked with either EtG or EtS……..……………………………………..………40 LIST OF TABLES Table Page 1. Retention Times (tR) and MS/MS parameters of EtG, EtS and internal standards, declustering voltage, and collision energies used for acquisitions………………16 2. Average signal-to-noise (S/N) ratio of EtG and EtS in urine diluted 1:10 up to 1:1000 (n=3)………………….…………………………………………………..29 3. Average absolute peak area for EtG and EtS in deionized water and 1:1000 diluted urine………………………………………………………….…………..35 4. Accuracy and intra-day and inter-day precision for quantification of EtG and EtS in 1:1000 diluted urine at three concentrations (0.050, 0.150, 0.500 μg/mL) determined for calibration curve prepared in deionized water……………………………………………………….…………………..…37 5. Accuracy and intra-day and inter-day precision for quantification of EtG and EtS in 1:1000 diluted urine at three concentrations (0.050, 0.150, 0.500 μg/mL) determined for calibration curve prepared in diluted blank urine……………………………………………………………….………...…...38 1 1. Introduction Alcohol and Alcohol Abuse Alcohol is the most commonly-abused, addictive substance (1) and causes serious public problems for people and countries. Alcohol abuse is a growing problem with relevant health, clinical and social implications all over the world. For example, driving under the influence of alcohol (DUI) is among the most serious of social problems (2). Thus, alcoholism, as one of the most frequent addictions, is of great interest in clinical and forensic medicine, and research efforts on ethanol consumption biomarkers is a growing field in forensic toxicology (3). Confirming alcohol (ethanol) intake is a major task in forensic toxicology and psychiatry (4). Measurement of ethanol in serum, blood, hair or urine is the standard way to detect alcohol consumption or monitoring abstinence (5). However, ethanol itself is rapidly eliminated from the body (6). Measurement of ethanol is limited to detecting only very recent consumption. Developing biomarkers of acute and chronic ethanol consumption with longer half lives in the human body and lower detection limits are needed. Alcohol biomarkers Testing of alcohol biomarkers is becoming an effective way to prove ethanol consumption. Most of the ethanol consumed is oxidized to acetaldehyde and acetic 2 acid, but a small part undergoes non-oxidative transformation (Figure 1) (6). In addition to carbohydrate deficient transferring, gamma glutamyl transferase, or mean corpuscular volume, numerous researchers focus on non-oxidative ethanol metabolites as biomarkers (7). Non-oxidative biomarkers include fatty acid ethyl esters (FAEEs), β-D-ethyl glucuronide (EtG), phosphatidyl ethanol (PEth), ethyl sulfate (EtS), and ethyl phosphate (EtP) (8-11). These biomarkers can be detected in various biological samples for extended periods following ethanol consumption. For example, FAEEs are detected in serum and blood up to 24 hrs after alcohol consumption (8). EtG exists in urine for up to 5 days and PEth can be detected in blood for more than two weeks following ethanol consumption (9). EtS and EtP, as newly developed biomarkers, have been under investigation in recent years (12-14). Unchanged in breath, urine and sweat < 5% < 0.1% CH3CH2OH Sulfotransferas UDP-glucuronosyl Ethyl glucuronide (EtG) -transferase (UGT) Ethanol (SULT) > 95% Ethyl sulfate (EtS) Alcohol and Aldehyde dehydrogenase CH3CHO + CH3COOH Acetaldehyde and Acetic acid Figure 1. Elimination pathways for ethanol in the human body, showing the major, oxidate route, and the minor conjugation reactions with sulfate and glucuronic acid 3 Although the above mentioned alcohol biomarkers are detected in many body fluids such as serum (15), sweat (16), blood (17) and urine (18) as well as hair (19), the most widely used and effective way for studying alcohol exposure monitoring is through urinary testing (20). Compared to ethanol, EtG and EtS are excreted in urine for prolonged periods of time, making them useful as sensitive urinary alcohol biomarkers. EtG is the first direct metabolite of ethanol to be found in human hair in 1993 by Sachs (21) and later by Schmitt et al (22). EtG (Figure 1 and 2) is a nonvolatile, water-soluble, polar, and relatively stable molecule that can be detected in biological fluids and tissues. It is formed by ethanol conjugation with glucuronic acid and is mediated by UDP-glucuronyl tranderases, a superfamily of highly polymorphic enzymes that are found mainly in the endoplasmic reticulum (23). It is estimated that only 0.02 to 0.06% of the ingested ethanol dose is recovered as EtG in human urine (24). Previous studies performed in human subjects indicated that the elimination of EtG occurred over a longer period of time than that of the parent compound, ethanol. Being a direct metabolite of alcohol, EtG is considered a specific marker of recent, short-term alcohol consumption that can be detected in urine up to 80h after alcohol consumption while the ethanol can no longer be detected (25). Therefore, the development of a rapid and reliable procedure for measuring EtG in urine is of great interest for forensic studies, as well as for traffic investigations involving alcohol consumption. 4 Another minor direct ethanol metabolite, EtS (Figure 1 and 2), is a newly discovered alcohol biomarker (26). EtS is formed by transfer of a sulfuric group from 3’-phosphoadenosine -5’-phosphosulfate to ethanol and is mediated by the family of sulfotransferases (27). Animal studies indicated that EtS is excreted in urine mainly during the first 24h, but can be excreted in urine for up to 30h (28). Because of the difference in the metabolic formation of EtG and EtS, each can be used to indentify recent ethanol consumption. Furthermore, the analysis of EtS, in addition to EtG, can be used as further confirmation of ethanol consumption. In addition, recent research suggested that bacterial urinary tract infection has less of an impact on EtS determination because EtG is more susceptible to bio-degradation in the urinary tract (29). Figure 2. Chemical structures and molecular formulas of EtG and EtS and pentadeuterated internal standards EtP, another newly discovered alcohol metabolite, has also been proposed to be used as a urinary biomarker (30). However, EtP was measured at elevated 5 concentrations for only a very short period of time (31). Therefore, EtP is a less sensitive biomarker than EtG or EtS and, to date, the use of EtP as a urinary biomarker of alcohol consumption is not reported, because its half life is roughly equivalence to that of ethanol. Thereby, EtG and EtS, which have similar urinary excretion profiles, are increasingly being used as urinary biomarkers indicating recent alcohol consumption. In urine, EtG was detectable for up to 10 times longer than ethanol, while EtS was detectable for up to 3~8 times longer than ethanol. Bicker et al. found a statistically significant linear correlation between EtG and EtS concentration in urine (32), which indicated they were both direct ethanol metabolites and had overlapping excretion time profiles in urine. Simultaneous measurement of EtG and EtS in urine is becoming an effective tool for monitoring alcohol consumption (20). In addition to use as biomarkers for alcohol consumption, EtG and EtS can also be regarded as high-specificity markers of alcohol exposure. Some recent reports about alcohol exposure indicated that alcohol may be absorbed into the body from the use of alcohol-containing mouthwash or frequent applications of alcohol-based hand sanitizers, and that EtG or EtS may consequently be present in the urine of individuals who only have these unintentional or accidental exposures to alcohol (33, 34). Department of Health and Human Services has advised that specificity studies at low EtG levels are needed for distinction of alcohol consumption and incidental alcohol exposure. Many of the studies often conclude that the presence of EtG and EtS are 6 indicative of monitoring alcohol consumption or exposure during withdrawal treatments or of situations where it is important to exclude alcohol use (eg. Pregnancy), but fall short of developing an accurate method to analyze the extent of alcohol intake in such a situation. The detection of small changes in concentrations of alcohol metabolites is becoming a necessity for the effective interpretation of alcohol exposure data. Therefore, it is important to develop a robust method for the quantification of EtG and EtS at the low parts per billion levels in urine to establish both the existence of alcohol consumption and the potential of other routes of alcohol exposure. Determination of EtG and EtS The first analytical method for analyzing EtG as a biomarker of ethanol consumption was reported by Schmitt et al.in the mid-1990s and was based on gas chromatography mass spectrometry (GC-MS) (22). The method required derivatization to convert EtG, the highly polar glucuronide conjugate, to a substance of higher volatility. The applicability of this technique to routine analysis remains uncertain because of the lack of validation based on the published method. Recently, non-GC-MS methods were developed and validated for the analyis of EtG and EtS including liquid chromatography mass spectrometry or tandem mass spectrometry (LC-MS or LC-MS/MS) (35), liquid chromatography with pulsed electrochemical detection (36), capillary zone electrophoresis (37), and 7 enzyme-linked immunosorbent assay (38). However, the non-MS methods are less selective than the MS-based methods (39). Comparing to other published methods, measurement of EtG and EtS by LC-MS/MS is a rapid and sensitive method that does not require time-consuming sample preparation procedures (such as derivatization) and is the technique of choice for measuring EtG and EtS simultaneously. However, depending on the amount of alcohol consumed, the time between drinking and urine sampling, and diuresis (24), the EtG and EtS concentration may vary considerably between, and within, individuals. It is necessary to remove interfering matrix constituents or, in case of urinary analysis, to pre-concentrate the analytes prior to analysis by LC-MS/MS. Current analytical published methods include sample pretreatment steps such as solid phase extraction (SPE) (40-43), “evaporate and reconstitute” (44, 45) and “dilute and inject” (32, 46, 47) approaches in connection with LC-MS/MS. SPE is commonly reported in analytical methodology for urinary analyses (40). Despite the advantages of SPE including commercial availability, concentration and clean-up of sample, some disadvantages exist with SPE like variable recoveries of analytes, introduction of potential interfering SPE extracts into the system, and the time and cost associated with performing SPE. Though “evaporate and reconstitute” approach affords efficient concentration, the complicated preparation and uncertain mass loss duing evaporation limit its application. “Dilute and inject” approach is developing as an effective way of cost effectiveness and rapid analysis for minimizing sample preparation steps in 8 recent years. Previous studies used a 1:2 to 1:50 dilution of urine with deionized water, methanol, acetonitrile, or ammonium acetate buffer. However, matrix effects still existed with dilution factors up to 50 (46) and a loss of sensitivity occurred due to limited sample injection volume (32). In addition, for the determination of alcohol metabolites with high polarity, such as EtG and EtS, it is very challenging to establish a reliable LC-MS/MS method because these polar compounds show poor retention on traditional columns prior to mass spectrometric detection. There are several reports on the determination of low parts per million levels of EtG and EtS in biological fluids and tissues in particular, for urine (42, 44-49). Although a wide variety of methods were used, and the detection limits are not always provided, the concentrations of EtG or EtS range from 0.100 μg/mL (44) to as high as 20 μg/mL (45). Recent reports for EtG in urine range as 0.05 μg/mL (LOD) to 5.0 μg/mL (46). So far, this is the lowest detection limit reported for EtG in urine available in the open literature. Large-volume injection Large-volume injection (LVI) has been used for the analysis of illicit and legal drugs at low concentrations (50). Large volume injection (LVI) is a technique that dates back to the early 1980s (51) and involves the direct injection of liquid samples larger (30 – 2000 μL) than the conventionally-injected volumes of 10 - 20 μL. The injection of a large volume of solvent of low elutropic strength containing the sample effectively acts as the initial mobile phase, thereby concentrating analytes onto the 9 head of the analytical column. The injection solvent (e.g., water or non-aqueous solvents), salts, and other matrix components do not partition into the stationary phase and flow, un-retained, through the column to waste rather than to the detector (52). After the injection phase, which is analogous to the sample concentration phase of SPE, the elutropic strength of the mobile phase is increased to elute and separate the concentrated analytes (53). The direct injection of aqueous sample volumes on an analytical column is similar to frontal chromatography. With LVI, a large sample volume (30-2000 μL), relative to the void volume of the column, is introduced continuously rather than as a small volume band at the head of the column. As a result, with LVI of aqueous samples, the low elutropic strength of the co-injected water entering the LC column results in focusing of the analytes at the head of the analytical column. The benefits of LVI are recognized for a variety of applications including the determination of phenylthiohydantoin-derivatized amino acids (54), biogenic amines (55), trace analysis of pesticides, and herbicides and fungicides in vegetables and soils (56). Additionally, LVI has been used for the determination of micropollutants in surface waters, including pesticides (57), herbicides (58), fungicides (59), and fluorinated alkyl substances (60). Previous work in our laboratory demonstrated the use of large volume injection (e.g., 1800 μL) for the analysis of illicit and legal drugs (61), polar organic contaminants such as fluorochemicals (62) in wastewater, and for the quantification of fullerenes using normal-phase LC (63). 10 LVI offers several advantages including increased sensitivity and accuracy and minimal sample handling since SPE is eliminated. In LVI, analyte pre-concentration and analytical separation are linked automatically by adding one or more stainless steel sampling loops to liquid chromatographs equipped with conventional, commercial auto-samplers that are capable of injecting volumes in the hundreds of microliters. Sample throughput is increased, at minimal cost and handling, compared to SPE because no SPE cartridges or standalone hardware are needed. In addition, the total sample volume required is smaller for LVI than for SPE because the entire sample is injected, whereas only a fraction of off-line SPE extracts are typically injected. Furthermore, method sensitivity can be improved when LVI is introduced into “dilute and inject” approach. Thus, using LVI coupled with direct injection of diluted urine instead of SPE as the sample cleanup procedure will be discussed and applied to investigate an improved analytical method for the analysis of EtG and EtS in urine. Summary The present work was aimed to develop and validate a rapid and sensitive analytical method based on LC-ESI-MS/MS and large-volume injection (900 μL) for the measurement of EtG and EtS in highly diluted urine. For this purpose, both chromatographic and instrumental parameters were optimized. Different urine dilution factors were tested and evaluated in order to minimize matrix effects. The method was optimized and evaluated by determining accuracy and precision through 11 the testing of spiked urine samples. The detection and quantification limits of the instrument and method detection limits were then determined using the optimized conditions. Matrix effects were eliminated by using 1:1000 dilution of urine with deionized water. Finally, the method was demonstrated and validated using third-party reference urine with certified EtG and EtS concentrations. 2. Experimental 2.1 Standards and Reagents Ethyl glucuronide (analytical grade >99%) and its deuterated standard, ethyl glucuronide-D5 (analytical grade >99%), were purchased from Cerilliant Corporation (Round Rock, TX) at concentrations of 1 mg/mL in methanol. Ethyl sulfate sodium salt (analytical grade >99%) and its deuterated standard, ethyl sulfate-D5 sodium salt (analytical grade >99%), were obtained from AthenaES (Baltimore, MD). HPLC grade methanol was purchased from Fisher Scientific (Fair Lawn, NJ). Formic acid was purchased from EMD Chemicals (Gibbstown, NJ). Ammonium acetate was purchased from Mallinckrodt Chemicals (Phillipsburg, NJ). The mobile phase of a buffer system of 0.1% formic acid and 15 mM ammonium acetate and 5% methanol was prepared daily and filtered through hydrophilic polypropylene membrane filters 0.45 μm purchased from Pall Corp (Ann Arbor, MI). 12 2.2 Preparation of Stock and Working Solutions Individual standard stock solutions were prepared by dilution into methanol and stored in the dark at -80◦C. The internal standards, EtG-D5 and EtS-D5, were prepared by dissolution of each compound in methanol at the concentration of 100 μg/mL. EtG and EtS working stock solutions were further prepared in methanol at the concentrations of 0.4, 1, 16, and 400 μg/mL by dilution. The working solutions were stored in the dark at -20 ◦C and showed no appreciable degradation over a two month period, with a maximum of ten freeze-and-thaw cycles. Small quantities of the standard and internal standard working solutions were kept at 4 ◦C for daily analysis and were replaced every two weeks. Two sets of calibration curves were prepared and determined by adding appropriate amounts of EtG and EtS standard solutions and 60 μL each of EtG-D5 and EtS-D5 (1 μg/mL) as internal standards. One calibration curve set was prepared in deionized water and the second set of calibration standards were prepared in 1:1000 diluted blank urine. Each calibration curve consisted of eight points for EtG (0.015, 0.05, 0.1, 0.25, 0.5, 1, 5, and 10 μg/mL,) and eight points for EtS (0.025, 0.05, 0.08, 0.1, 0.25, 0.5,1 and 5 μg/mL). The EtG and EtS concentrations correspond to 0.015-10 mg/mL and 0.025-5 mg/mL in undiluted urine. The linearity of the calibration curve was determined by plotting peak area ratios of the analytes to internal standards against nominal concentrations of the analytes and was estimated by a 1/x weighing factor. 13 Instrumental blanks consisted of deionized water containing no standards or internal standards. EtG and EtS standards at three concentration levels: 0.05 μg/mL(low), 0.15 μg/mL (medium), and 0.5 μg/mL(high) were used as quality control samples. Blanks and quality control samples were run within each sequence to monitor carryover, instrument background and sample preparation and all blanks during the study were blank (no signal above baseline or at an S/N > 3). 2.3 Sample Preparation Blank Urine Toxicology Control A blank freeze-dried urine toxicology control sample was purchased from UTAK under the name DAU (Lot # 1502) that was certified as free of EtG and EtS (UTAK Laboratories, Valencia, CA, USA). It came as a dried material that was used as the reference blank urine. The dried blank UTAK control material was reconstituted by dissolving the material into 10 mL of deionized water as per the manufacturing instruction. The urine control material was stored in the dark at -20 ◦C. Spiked blank urine samples were prepared freshly following a standard procedure: appropriate amount of the working standard solution of EtG and EtS was added to the reconstituted blank urine sample. It was then diluted with deionized water based on dilution factor of 1:1000. After dilution, a 2 mL aliquot volume of diluted blank urine was then centrifuged in an Eppendorf centrifuge 5415 C for 30 min at a maximum speed of 14,000 rpm (10,000 g). An aliquot of 1.2 mL of supernatant was then 14 transferred into a 2 mL autosampler glass vial and spiked with 60 μL of each stable-isotope labeled internal standard to give a final concentration of 50 μg/L of EtG-D5 and EtS-D5. The vials were transferred to an Agilent 1100 sample tray and analyses were carried out within 24 hrs of sample preparation. Certified UTAK Urine Control The UTAK urine toxicology control with certified EtG and EtS concentrations of 50.0 mg/L (Lot# 3204), was purchased and received as a liquid and used as an external reference standard for quality control purposes (UTAK Laboratories, Valencia, CA, USA). The certified UTAK urine control sample was stored in the dark at -20 ◦C. The certified UTAK urine control sample with a known EtG and EtS concentration was diluted directly with deionized water based on dilution factor of 1:1000 and processed as described above. 2.4 Instrumentation 2.4.1 High Pressure Liquid chromatography (HPLC) HPLC analyses were performed with an Agilent 1100 series system (Agilent Technologies, Santa Clara, CA). The HPLC instrumentation was composed of a vacuum degasser, a binary pump, and auto-sampler maintained at 4 ºC. Large-volume injections and separations were conducted on this system that had been modified by the addition of a commercially-available 900 μL “Injection Upgrade Kit” (Agilent 15 part no. G1363A) that consisted of a 900 μL analytical head, a 900 μL stainless steel sample loop extension, and a 900 μL needle. Chromatographic separation was carried out using an Agilent Zorbax-SBAq column (150╳4.6 mm I.D., 5μm particle size) equipped with 2.0╳4.0 C18 security guard column (Phenomenex,Torrance, CA) to protect the separation column. The column was kept at 30 ºC during analysis. The flow rate was 500 μL/min. The injection volume was 900 μL, and the mobile phase consisted of a buffer system of 0.1% formic acid and 15 mM ammonium acetate (A) and 5% methanol (B) in isocratic mode for a total run time of 18 min. 2.4.2 Electrospray Tandem Mass spectrometry (ESI-MS/MS) Detection and quantification were performed on a Waters Micromass tandem mass spectrometer (Milford, MA) with an electrospray ionization (ESI) source operated in negative ionization and multiple reaction monitoring (MRM) mode. Nitrogen and argon were used as nebulizing and collision gases, respectively. The following conditions were used in the mass spectrometer: source temperature, 150 °C; desolvation gas temperature, 450 °C; capillary voltage, 3.57 kV; extractor voltage, 3 V; RF lens voltage, 0.2 V; cone gas flow, 25 L/h; desolvation gas flow, 650 L/h; ion energy, 0.5 V; ion energy, 2.0 V; and entrance and exit potential, 11 V and 25 V. An interchannel and scan delay of 0.03 s between groups of transitions was used to enhance MS sensitivity. 16 Table 1. Retention times (tR) and MS/MS parameters of EtG, EtG-D5, EtS and EtS-D5, declustering voltages (V), and collision energies (eV) used for acquisitions Analyte tR (min) MRM pair Declustering Collison Voltage (V) Energy (eV) EtG 7.61 221.1/75 .0* -20 −15 221.1/84.9 -20 -15 221.1/113.2 -20 -15 EtG-D5 7.61 226.0/75 .0* -20 -15 EtS 8.87 125.0/96.9* -20 -15 125.0/79.9 -20 -25 130.0/97.9* -15 -15 130.0/79.9 -20 -30 EtS-D5 8.87 * MRM pairs for quantification A total of eight transitions were acquired to quantify EtG and EtS analytes with appropriate MRM parameters (Table 1). The mass transitions 221→75.0, 221→84.9 and 221→113.20 were selected for EtG while 226→75.0 was selected for EtG-D5 (internal standard). For EtS, 125.0→96.9 and 125.0→79.9 were selected for EtS while 130→97.9 and 130.0→79.9 were selected for EtS-D5 (internal standard). The 17 transitions m/z 221→75.0 and m/z 226→75.0 were used to quantify EtG and EtG-D5, respectively. The transitions m/z 125→96.9 and m/z 130→97.9 were used to quantify EtS and EtS-D5, respectively. The remaining transitions were used as visual checks for confirmation. The peak retention times of EtG and EtS at 7.61 min and 8.87 min, given in the Table 1, were used to determine the appropriate time windows for each group of transitions monitored in the MRM mode. The characteristic precursor ions of EtG and EtG-D5 in ESI negative mode are the deprontonated molecular ions [M-H]- m/z 221 and m/z 226, respectively, and are consistent with ions observed by others (18,32). The most abundant product ions for EtG (m/z 75.0, 84.9, 113.2) and EtG-D5 (m/z 75.0) may come from the fragmentation of glucuronic aicd. The characteristic precursor ions of EtS is m/z 125 and the product ions are m/z 96.9 [HSO4]- and m/z 79.9 [SO3]- . The precursor ion of EtS-D5 is m/z 130 and product ions are m/z 97.9 [DSO4]- and m/z 79.9 [SO3]- (Figure 3 and Figure 4). 18 (A) EtG (B) EtG-D5 Figure 3. Product-ion spectra of EtG (A) and EtG-D5 (B) (A) EtS (B) EtS-D5 Figure 4. Product-ion spectra of EtS (A) and EtS-D5 (B) 19 2.5 Injection Volume and Dilution Factor Optimization Five injection volumes (100, 500, 900, 1200 and 1400 μL) of EtG and EtS standards in deionized water were tested to determine the optimum injection volume. To reach a capacity of more than 900 μL, a commercially-available 1400 μL stainless steel seat extension loop (Agilent part no. G13G13-87308) was installed between the seat capillary fitting and port 5 (injection valve) of the analytical head (Figure 5). Figure 5. Modified injection of an Agilent 1100 HPLC with the locations of the 1400 μL stainless steel seat extension loop and seat capillary indicated. The 1,400 μL seat-extension loop was not necessary for sample injection volumes of 900 μL or less. For injection volumes of 1,200 μL or greater, a injection progam was initiated. A needle wash was followed by the withdrawal of 600 μL of sample 20 that was injected into the 1,400 μL seat capillary. This step was followed by the withdrawal of an additional 600 μL to 800 μL to give a total sample injection volume of 1,200 μL and 1,400 μL. For all analyses, the divert valve, located after the analytical column and before the ESI interface, was switched to waste for the last five min of each chromatographic analysis to protect the detector from unwanted material. To minimize the matrix effects of urine, different dilution factors of urine were tested. Blank urine samples, spiked with EtG and EtS, were diluted with deionized water by five different dilution factors (1:10, 1:50, 1:200, 1:500, and 1:1000 (Vol/Vol)) in order to obtain a final concentration of 050 μg/mLfor EtG and EtS and analyzed by LC-MS/MS using a 900 μL injection volume. 2.6 Specificity Method specificity was checked by analyzing blank urine samples spiked either with analytes in the absence of IS and with IS in the absence of analytes. Eight different samples: four blank urine sample (neither analytes or IS), two blank urine sample spiked with EtG-D5 and EtS-D5 only, and two blank urine sample spiked with 0.05 μg/mL of EtG and EtS and no IS were analyzed by the optimized LVI of 900 μL and a dilution factor of 1:1000 to identify possible interfering peaks in the urine matrix or standards. 2.7 Stability After sample preparation, samples may remain in an auto-sampler tray for up to 24 hr before direct injection into the LC-ESI-MS/MS system for analysis. In order to 21 investigate potential degradation during this time period, spiked urine samples were analyzed over a 24 hr period at three concentration levels (0.050, 0.150, 0.500 μg/mL, n=3 each). The immediate analysis results (time = 0 h) and the EtG and EtS absolute peak areas were used as the reference. The peak area of the analyte was plotted against time to determine if the EtG or EtS degraded in the auto-sampler tray at room temperature. The mean peak area at each time point was not significantly different from the initial time point during the 24 hr period. These findings confirmed that both EtG and EtS were stable during the 24 hr analysis period at room temperature and were with regard to EtG and EtS complying with earlier data (35, 46). 2.8 Matrix Effects The matrix effect of diluted urine (1:1000) was evaluated by analyzing 1:1000 diluted spiked blank urine with EtG and EtS, at four concentration levels including 0.01, 0.05, 0.25 and 1.0 μg/mL. Raw peak area of EtG and EtS were compared to raw peak area for standards in deionized water at equivalent concentrations. The concentrations of analytes in diluted urine corresponded to 10, 50, 250 and 1000 μg/mL in undiluted urine. 2.9 Validation Accuracy, defined as recovery, was determined by spiking three replicates of 1:1000 diluted urine containing 0.05, 0.15, and 0.5 μg/mL each of EtG and EtS. These three concentrations corresponded to concentrations in undiluted urine of 50, 150, 500 μg/mL. 22 Intra-day precision, calculated as the relative standard deviation (RSD), was determined for three replicates (n=3) at each of three concentrations (0.050, 0.150, 0.5 μg/mL) prepared in 1:1000 diluted urine samples on a single day. Inter-day precision was determined by analyzing three replicates of spiked urine aliquots at same concentrations, prepared freshly on a daily basis over four consecutive days during a single week. The concentrations of the analytes used to determine accuracy and precision corresponded to low, medium and high concentrations used in the calibration curves Instrument detection limits (IDL) for EtG and EtS, defined as the concentration needed to achieve a signal/noise (S/N) ≥ 3, were determined by analyzing standards in deionized water ranging from 0.001 μg/mL to 0.05 μg/mL based on linear regression. The method limit of quantification (LOQ), defined as the concentration in diluted urine that gave a S/N ≥10, were determined by analyzing spiked 1:1000 dilute urine samples that varied in concentrations from 0.005 μg/mL to 0.05 μg/mL. 3. Results and Discussion 3.1 Method Development 23 An effective sample cleanup (like SPE) and analyte enhancement from urinary matrix was considered to be difficult and presumably lengthy because of the high polarities of EtG and EtS, and the presence of inorganic and organic anions in urine with similar extraction or chromatographic properties. Therefore, a high-throughput analytical method based on direct injection of large sample volume of diluted urine was developed. This strategy required improvements in chromatography in order to sufficiently separate EtG and EtS from urinary matrix components. Thus, the effects of the chromatographic column, mobile phase composition, injection volume and sample dilution factors on chromatographic performance and overall method performance were determined. 3.1.1 Chromatography In this research, a new commercially available Agilent ZORBAX SB-Aq, silica-based reversed phase LC column was used to increase the chromatographic retention of EtG and EtS (Figure 6). EtG and EtS are polar compounds (Figure 1), making them amenable to separation on an LC column with a hydrophilic stationary phase. Satisfactory separation of EtG and EtS in diluted (1:1000) spiked blank urine were achieved using a 900 uL injection volume on the Zorbax SBAQ column. The instrument run times were 18 min, including LC column washing, separation and re-equilibration. This column retained EtG and EtS to a greater extent than other conventional reversed phase columns (33, 62). The ZORBAX SB-Aq column has a hydrophilic surface that inhibits phase collapse, even in 100% aqueous mobile phases. 24 EtG 221.1-75.0* EtG 221.1-84.9 EtG 221.1-113.2 EtG-D5 226.0-75.0* % EtS 125.0-96.9* EtS 125.0-79.9 EtS-D5 130.0-97.9* EtS-D5 130.0-79.9 2 4 6 8 10 Time (min) 12 14 16 Figure 6. Chromatograms of EtG (0.08 μg/mL), EtG-D5, EtS (0.08 μg/mL) and EtS-D5 in a spiked urine sample with a 900 μL injection volume with MRM transitions indicated. Previously, published methods describe the use of reversed phase LC columns that gave poor chromatographic retention or the use of self-made LC columns that are not commercially available for routine analysis. For example, Helander and Beck (14) used a Hypercarb column for which the retention of EtG and EtS was insufficient and eluted close to the void volume. Dresen (64) used a polar-endcapped phenylpropyl reversed phase column that gave good retention of the analytes with EtG eluting at 4.1 min and EtS eluting at 4.8 min. However, this method required a postcolumn 25 addition of acetonitrile to enhance the ESI sensitivity. Other previously published methods for separating EtG and EtS include an acryamido-type hydrophilic column (TSKgel Amide-80) with a split of the eluate (44), an octadecylsilyl column (Chrompack Inertsil ODS-3) with isocratic elution (47), and a self-made mixed-mode RP/weak anion exchange stationary phase based on N-(10-undecenoyl)-3amomioquinuclidine bonded to thiol- functionalized silica particles with isocratic elution (32). 3.1.2 Optimization of Mobile phase Initial mobile phase compostion consisted of aqueous 0.1% formic acid (vol/vol), which gave retention times of 9.2 min for EtG and 11.3 min for EtS. Given the selectivity of the mass spectrometer, this chromatographic separation was adequate. However, variable retention times were observed when the mobile phase contained only 0.1% formic acid. The addition of ammonium acetate was explored in order to increase the pH of the buffer, and to improve peak shape while maintaining sufficient chromatographic separation of EtG and EtS. Therefore, the effect of adding ammonium acetate to the mobile phase was using 5 mM to 30 mM ammonium acetate in the 0.1% formic acid buffer (Figure 7). 26 (A ) 5 mM EtS EtG % 2 4 6 10 8 12 14 Time (min) (B) )10mM EtS EtG % 2 4 10 8 6 12 14 Time (min) (C) 15 mM EtS % EtG 2 4 6 8 Time (min) 10 12 14 27 (D) 30 mM EtS % EtG 2 4 6 8 10 12 14 Time (min) Figure 7. Chromatograms of EtG and EtS spiked into 1:1000 diluted blank urine and separated with different ammonium acetate concentration in the 0.1% formic acid mobile phase including: (A) 5 mM ammonium acetate, (B) 10 mM ammonium acetate, (C) 15 mM ammonium acetate, and (D) 30 mM ammonium acetate. Chromatographic retention times (tR) were reproducible with the addition of 10 mM or greater ammonium acetate. Higher ammonium acetate concentrations resulted in a decrease in the mass spectrum base peak intensity, while lower ammonium acetate concentrations resulted in decreased chromatographic resolution of EtG and EtS. Therefore, as a compromise between sensitivity and selectivity, 15 mM ammonium acetate was added to the aqueous 0.1% formic acid mobile phase. Although tailing of the EtS peak (Figure 7) was observed, the retention of EtG improved its detection by an almost one order of magnitude, as indicated by increased signal-to-noise ratios (S/N), because of less background noise in the detection 28 window. With the addition of 15 mM ammonium acetate, the retention times of EtG and EtS were 7.5 min and 8.6 min, respectively. This improved performance maybe due to the increase pH or ionic strength. In addition, the ammonium acetate may mask the silanol moieties on the stationary phase. 3.1.3 Optimization of Injection Volume Using 0.1% formic acid with 10 mM ammonium acetate as the mobile phase and a ZORBAX SB-Aq LC column, peak shape and resolution of EtG and EtS were satisfactory and the injection volume could be optimized. Upon injecting five different urine sample volumes including 100, 500, 900, 1200 and 1400 μL, it was determined that peak shape of the analytes was symmetrical, with little or no evidence of band broadening when the sample injection volume was 900 μL or less. In addition, the EtG and EtS retention times were reproducible for 900 μL injection volumes. However, when sample injection volumes were increased to 1200 μL or more, the EtS peak shape became broad and tailed. Furthermore, there was a breakthrough of EtS observed with injection volumes of 1400 μL. In order to obtain the best reproducibility and sensitivity, 900 μL was chosen as the final injection volume and was used for all subsequent experiments and analyses. A 900 μL injection volume is up to 180 fold higher than that of the pervious studies that ranged from 5 μL to 15 μL (32, 44, 46, and 64). 29 3.1.4 Optimization of Sample dilution factor Urine’s high and variable ionic strength prevented direct injection without sample dilution. A research goal was to optimize the dilution factor of the urine sample to allow for injection of the greatest sample volume or concentration on the analytical column possible without deteriorating chromatographic separation or increasing the background noise (or decreasing the S/N). Table 2. Average signal-to-noise (S/N) ratio of EtG and EtS in urine diluted 1:10 up to 1:1000 (n=3). S/N ratio Dilution factor EtG EtS 10 3.8 ND* 50 10.3 8.5 200 63.2 54.1 500 166.7 99.6 1000 198.2 121.5 * ND represents not detectable The EtG and EtS S/N ratios were compared at the same analyte concentration of 0.050 μg/mL by spiking EtG and EtS after the urine sample was diluted by five 30 different dilution factors from 1:10 to 1:1000 (vol/vol) (Table 1). In this experiment, the final concentration and therefore the mass injected using a 900 μL injection volume was constant while the matrix varied. The S/N values increased from 3.8 to 198.2 for EtG and from not detected to 121.5 for EtS when increased the dilution factor from 10 to 1,000. The increase in S/N for higher dilutions while keeping the mass injected constant indicated greater sensitivity. Therefore, a dilution factor of 1:1000 was chosen in order to maximizing sensitivity while minimizing matrix effects. While a higher dilution factor was accompanied by a loss in the sensitivity, Bicker et. al. (32) combined two different sample dilution factors 1:20 and 1:1000 as a balanced approach to minimize the matrix effects as well as obtaining enough sensitivity for effective measurement of real urine samples. However, from my study sensitivity was well maintained because of the large injection volume of 900 μL used with the high 1:1000 dilution factor and these conditions were used for all subsequent experiments and analyses. 3.2 Method Validation 3.2.1 Specificity The specificity or selectivity of the analytical method, the ability of an analytical method to differentiate or quantify the analyte in the presence other components in the sample, was determined (Figure 8). Chromatograms in Figure 8 show the MRM 31 chromatograms of blank urine, blank urine plus IS, and blank urine spiked with 0.050 μg/mL EtG and EtS. Chromatograms of A, C, E and G indicate the absences of EtG, EtS, EtG-D5 and EtS-D5 in the blank urine while chromatograms of B, D, F and H show the presences of each analyte. There was no significant interference caused by endogenous substances from the urine in the EtG, EtS, EtG-D5 or EtS-D5 retention time windows. These results indicate that this analytical method provided acceptable specificity while the analytes were well distinguished and separated. (A) 221→75 (C) 125→97 (E) 226→75 (G) 130→98 (B) 221→75 EtG (D) 125→97 EtS (F) 226→75 EtG-D5 (H) 130→98 EtS-D5 Figure 8. MRM chromatograms of EtG, EtS, EtG-d5 and EtS-D5 in blank urine (A, C, E and G) and spiked blank urine (diluted 1:1000) with a final concentration of 0.05 μg/mLfor each analyte (B, D, F and H). 32 3.2.2 Linearity Two calibration curves were constructed in (1) deionized water and (2) 1:1000 diluted blank urine. The ratio of the peak area of the analyte to that of the IS was proportional to concentration of the analyte from 0.015 to 10 μg/mL for EtG, and 0.025 to 5 μg/mL for EtS. A linear regression model was used to describe the regression relationship and different weighing factors (1/x, 1/x2, and none) were examined for the best linear fit of the calibration curve. A 1/x weighing factor was applied. Calibration curves with good linearity of the quantification of EtG and EtS in deionized water and diluted blank urine samples were shown in Figure 9. 100 diluted blank urine deionized water 80 area) Response factor (Analyte area/IS 120 60 (A) 40 20 0 0 1 2 3 4 5 6 7 EtG concentration (μg/mL) 8 9 10 11 33 Response factor (Analyte area/IS area) 100 90 80 diluted blank urine 70 deionized water 60 50 40 (B) 30 20 10 0 -0.5 0.5 1.5 2.5 3.5 4.5 5.5 EtS Concentration (μg/mL) Figure 9. Representative calibration curves in deionized water and 1:1000 dilute blank urine for EtG (A) and EtS (B). Representative equations obtained with deionized water were y=11.224 x + 0.5977 (R2=0.9992) (EtG), y=17.396x + 0.1255 (R2=0.9998) (EtS) while typical equations with diluted blank urine were y=11.131x + 0.5836 (R2= 0.9996) (EtG), y= 17.251x 0.1878 (R2= 0.9997) (EtS). Typical coefficients of determination (r2) for EtG and EtS were ≥ 0.999. The linear range (0.015 to 10 μg/mL for EtG and 0.025 to 5 μg/mL for EtS) were selected to represent the range of EtG (15 to 10,000 μg/mL) and EtS (25 to 5,000 μg/mL) concentrations observed in urine from subjects who have ingested alcohol (17, 32, and 48). 34 3.2.3 Matrix effects Endogenous compounds in the urine matrix can suppress or enhance ionization of the analyte. Matrix effects may impair method reliability and limit precision, accuracy and reproducibility. Ion suppression or enhancement is very common in atmospheric pressure sources, especially ESI. Previous studies for the analaysis EtG and EtS in urine using LC-ESI-MS/MS indicate matrix effects but that are normally compensated for using internal standards (45, 46, 48, and 64). Matrix effects were estimated by comparing the absolute chromatographic peak area of each analyte spiked in deionized water to the equivalent concentrations in spiked urine. In equation (3), Aurine is the absolute peak area of the analyte in the spiked urine, and Awater is the absolute peak area of the analyte in deionized water. Ion suppression or enhancement (%) = (Aurine - Awater) / Awater × 100 (3) In Table 3, a positive value in the ion suppression/ enhancement column indicates that diluted urine induced ion enhancement effects, while negative value indicates the presence of ion suppression effects. By diluting the urine with a dilution factor of 1:1000, matrix effects, either ion suppression or enhancement, were overall minimized to less than 8.33% (EtG) and 10.46% (EtS), which is comparable to the inter-day precision in Table 4 and 5. 35 Table 3. Average absolute peak area for EtG and EtS in deionized water and 1:1000 diluted urine. Analyte concentrations Awater a Aurine a (μg/mL) EtG EtS a Statistically Ion suppression or equivalentb enhancement (%)c 0.01 560±80 607±63 Yes 8.33 0.05 2124±190 2291±223 Yes 7.87 0.25 12601±890 12024±917 Yes -4.58 1.0 52148±1147 52429±537 Yes 1.63 0.01 1524±111 1683±94 Yes 10.46 0.05 8576±166 8427±214 Yes -1.73 0.25 41813±1997 38413±2501 Yes -8.13 1.0 154580±2193 159094±2212 Yes 2.92 Mean ± 95% CI (n=3); b based on t-test ; C Calculations based on mean value of absolute peak area of spiked blank urine samples versus the analyte response from deionized water (n=3); Furthermore, the mean absolute peak areas of EtG and EtS in diluted urine were statistically equivalent at the 95 % CI to those in deionized water, which indicated that the large volume injection of a 1:1000 dilution eliminated matrix effects. Because 36 matrix effects were eliminated, quantification of EtG and EtG in diluted urine can be performed using calibration standards prepared in deionized water. The eliminated matrix effects for 1:000 diluting were also demonstrated by Bicker et. al. (32) showing a deviation less than 5% for the mean absolute peak area of IS compared to that of water. However, the calibration standards were still prepared in dilute blank urine during their research because of the insufficient sensitivity with the small injection volume, which brought the additional process and cost. 3.2.4 Accuracy and Precision Accuracy and intra- and inter-day precision were determined by analyzing replicate spiked diluted urine samples at three different EtG and EtS concentrations (0.05, 0.15, and 0.5μg/mL). For purposes of comparison, accuracy, as determined by EtG and EtS recovery, was computed using equation (1) from calibration curves prepared in deionized water and dilute blank urine. The precision, as indicated by relative standard deviations (RSD, %), was calculated using equation (2) as the standard deviation of the measured concentration relative to the measured concentration, expressed as a percent of the standard deviation divided by the mean of measured concentrations. Accuracy (%) = (Conc. measured- conc. spiked)/conc. spiked ×100 (1) Precision (RSD, %) = Standard deviation of conc. measured/conc. measured × 100 (2) 37 Table 4. Accuracy and intra-day and inter-day precision for quantification of EtG and EtS in 1:1000 diluted urine at three concentrations (0.050, 0.150, 0.500 μg/mL) determined for calibration curve prepared in deionized water. Analyte EtG EtS a Nominal Concentration Accuracy b Intra-day Inter-day conc. measured.a (%) precisionb (%) precisionb (%) (μg/mL) (μg/mL) 0.050 0.050±0.006 99.9 5.1 4.5 0.150 0.150±0.004 99.8 1.2 8.3 0.500 0.509±0.019 102 1.5 11 0.050 0.051±0.002 102 1.6 5.8 0.150 0.148±0.005 98.7 1.3 11 0.500 0.501±0.037 100 3.0 8.7 Mean ±95% CI (n=3); b n=3 The results summarized in Table 4 and Table 5 indicate good precision and accuracy for the measurement of EtG and EtS in human urine based on two calibration curves using this analytical method. Furthermore, concentrations of EtG and EtS determined from these two calibration curves prepared in deionized water and diluted blank urine were equivalent at the 95% CI. Therefore, the method was accurate with overall recoveries ranged from 99.8% to 103% for EtG and 98.7% to 38 102% for EtS (Table 4). When quantifications from calibration curve prepared in diluted blank urine were performed, similar accuracies were obtained (Table 5). Quantification can be performed using calibration curves prepared in deionized water. Table 5. Accuracy and intra-day and inter-day precision for quantification of EtG and EtS in 1:1000 diluted urine at three concentrations (0.050, 0.150, 0.500 μg/mL) determined for calibration curve prepared in diluted blank urine. Analyte EtG EtS a Nominal Concentration Accuracy b Intra-day Inter-day conc. measured.a (%) precisionb (%) precisionb (%) (μg/mL) (μg/mL) 0.050 0.050±0.006 101 5.0 4.6 0.150 0.154±0.014 103 3.7 8.3 0.500 0.499±0.024 99.8 1.9 14 0.050 0.047±0.012 93.3 10.2 6.4 0.150 0.147±0.007 98.2 2.0 1.6 0.500 0.512±0.031 103 2.4 3.2 Mean ±95% CI (n=3); b n=3 Intra-day precisions were less than 5.1% for EtG and less than 3.0% with an average of 4.9% for EtS (Table 4). The inter-day precisions were less than 11% for 39 both EtG and EtS. Similar RSD values also obtained from the quantification based on the calibration curve prepared in diluted blank urine (Table 5). The RSD values are similar to those reported for the analysis of EtG and EtS in urine by LC-MS/MS either using SPE-based technology at additional cost (40) or without using high dilution and LVI at less sensitivity (32). 3.2.5 Detection and Quantification Limits The instrument detection limit (IDL) was 0.005 μg/mL for EtG and 0.01 μg/mL for EtS, which is a factor of 10 (or higher) lower than current published methodology for EtG and EtS (14, 64). The method LOQ was defined as the lowest concentration in the calibration curve and that gave an S/N ≥10 in diluted urine. The LOQ was 0.015 μg/mL for EtG and 0.025 μg/mL for EtS in 1:1000 diluted urine, corresponding to 15 μg/mL for EtG and 25 μg/mL for EtS in undiluted urine. The LOQs determined for the LVI method presented here are in the same or lower values as previous methods that used either SPE or low dilution (up to 1:50) as pretreatments for urine samples (14, 32, 40, 45, 46, 48,and 64). 3.3 Method Verification The analytical method was used to measure EtG and EtS in UTAK urine control samples with certified concentrations of 50 μg/mL. The chromatograms in Figure 10 showed the chromatographic comparison of EtG and EtS in the UTAK urine control sample and blank urine samples. 40 EtG EtS (A) Urine control (B) Blank urine Figure 10. LC-ESI-MS/MS chromatograms of (A) dilute reference certified urine containing 0.05 μg/mL EtG and EtS, and (B) blank urine that was not spiked with either EtG or EtS. The measured concentrations of EtG and EtS in 1:1000 diluted urine samples at 0.050 μg/mL (corresponding to an initial concentration of 50 μg/mL) matched the UTAK certified concentration at the 95%CI. The measured concentrations for the certified reference urine were 0.049 ± 0.013 μg/mL for EtG and 0.050 ± 0.003 μg/mL for EtS based on calibration curve prepared in deionized water. 0.050 ± 0.015 μg/mL for EtG and 0.049 ± 0.002 μg/mL for EtS were obtained using calibration curves prepared in 1:1000 diluted blank urine. Equivalent concentrations of EtG and EtS at 41 the 95% CI were obtained from calibration curves prepared in deionized water and diluted urine, which demonstrate the method accuracy using calibration curves prepared in deionized water for a cost effective and quantitative analyses. 4. Conclusions An analytical method for the simultaneous detection, quantification and confirmation of EtG and EtS in human urine samples using LC-ESI-MS/MS with LVI was developed, fully validated, and demonstrated. The method consisted of 900 μL injection volume, isocratic LC separation, tandem mass spectrometric detection, and quantification of EtG and EtS. The direct injection of 1:1000 diluted urine samples allowed for an increase in sample throughput while eliminating matrix effects. No interfering peaks were found throughout the experiments, indicating good specificity of the HPLC-ESI-MS/MS method for the simultaneous measurement of EtG and EtS. Selectivity was ensured by monitoring MRM transitions of the precursor ions for both EtG and EtS. The instrumental detection limit was 0.005 μg/mL for EtG and 0.010 μg/mL for EtS, a factor of 10 lower than current published methodology for EtG and EtS. The LOQ was 0.015 μg/mL for EtG and 0.025 μg/mL for EtS in 1:1000 diluted urine, which corresponded to 15 μg/mL for EtG and 25 μg/mL for EtS in undiluted urine. Finally, the method accuracy and precision were demonstrated by obtaining statistically-equivalent concentrations to that for certified third-party reference urine 42 from a commercial source. The method was accurate, rapid, cost-effective and reproducible without any sample pretreatment procedures. 5. Acknowledgements The author thanks Edward Kim, Dawn Fulton and Kelly Lenore from Agilent for HPLC column selections and method improvement in this work. 43 6. References (1) Wurst, F. M.; Metzger, J.; Marker, W. I. S. S. T., The ethanol conjugate ethyl glucuronide is a useful marker of recent alcohol consumption. Alcoholism-Clinical and Experimental Research 2002, 26, (7), 1114-1119. (2) Wurst, F. M.; Tabakoff, B.; Alling, C.; Aradottir, S.; Wiesbeck, G. A.; Muller-Spahn, F.; Pragst, F.; Johnson, B.; Javors, M.; Ait-Daoud, N.; Skipper, G. E.; Spies, C.; Nachbar, Y.; Lesch, O.; Ramskogler, K.; Hartmann, S.; Wolfersdorf, M.; Dresen, S.; Weinmann, W.; Hines, L.; Kaiser, A.; Lu, R. B.; Ko, H. C.; Huang, S. Y.; Wang, T. J.; Wu, Y. S.; Whitfield, J.; Snell, L. D.; Wu, C.; Hoffman, P. L., World Health Organization/International Society for Biomedical Research on Alcoholism study on state and trait markers of alcohol use and dependence: Back to the future. Alcoholism-Clinical and Experimental Research 2005, 29, (7), 1268-1275. (3) Wurst, F. M.; Kelso, E.; Weinmann, W.; Pragst, F.; Yegles, M.; Poromaa, I. S., Measurement of direct ethanol metabolites suggests higher rate of alcohol use among pregnant women than found with the AUDIT - a pilot study in a population-based sample of Swedish women. American Journal of Obstetrics and Gynecology 2008, 198, (4), -. (4) Wurst, F. M.; Vogel, F.; Jachau, K.; Varga, A.; Alling, C.; Alt, A.; Skipper, G. E., Ethyl glucuronide discloses recent covert alcohol use not detected by standard testing in forensic psychiatric inpatients. Alcoholism-Clinical and Experimental Research 2003, 27, (3), 471-476. (5) Skipper, G. E.; Weinmann, W.; Thierauf, A.; Schaefer, P.; Wiesbeck, G.; Allen, J. P.; Miller, M.; Wurst, F. M., Ethyl glucuronide: A biomarker to identify alcohol use by health professionals recovering from substance use disorders. Alcohol and Alcoholism 2004, 39, (5), 445-449. (6) Helander, A.; Beck, O., Ethyl sulfate: A metabolite of ethanol in humans and a potential biomarker of acute alcohol intake. Journal of Analytical Toxicology 2005, 29, (5), 270-274. 44 (7) Wurst, F. M.; Wiesbeck, G.; Forster, S.; Bechtel, G.; Wolfersdorf, M.; Huber, P.; Alexson, S.; Gilg, T.; Jachau, K.; Varga, A.; Alling, C.; Skipper, G.; Pragst, F.; Auwarter, A.; Weinmann, W., Further significance for the diagnostic and therapeutic usefulness of the non oxidative direct ethanol metabolites ethyl glucuronide (EtG), fatty acid ethyl esters (FAEEs) and phosphatidyl ethanol (PEth) in comparison to traditional markers. Pharmacopsychiatry 2003, 36, (5), 275-275. (8) Pragst, F.; Yegles, M., Determination of fatty acid ethyl esters (FAEE) and ethyl glucuronide (EtG) in hair: A promising way for retrospective detection of alcohol abuse during pregnancy? Therapeutic Drug Monitoring 2008, 30, (2), 255-263. (9) Politi, L.; Leone, F.; Morini, L.; Polettini, A., Bioanalytical procedures for determination of conjugates or fatty acid esters of ethanol as markers of ethanol consumption: A review. Analytical Biochemistry 2007, 368, (5), 1-16. (10) Jurado, C.; Soriano, T.; Gimenez, M. P.; Menendez, M., Diagnosis of chronic alcohol consumption - Hair analysis for ethyl-glucuronide. Forensic Science International 2004, 145, (2-3), 161-166. (11) Yegles, M.; Labarthe, A.; Auwarter, V.; Hartwig, S.; Vater, H.; Wennig, R.; Pragst, F., Comparison of ethyl glucuronide and fatty acid ethyl ester concentrations in hair of alcoholics, social drinkers and teetotallers. Forensic Science International 2004, 145, (2-3), 167-173. (12) Wurst, F. M.; Wiesbeck, G. A.; Alling, C.; Aradottir, S.; Pragst, F.; Johnson, B.; Javors, M.; Alt-Daoud, N.; Skipper, G. E.; Spies, C.; Nachber, Y.; Leach, O.; Ramskogler, K.; Hartmann, S.; Wolfersdorf, W.; Lauer, J.; Halter, C.; Weinmann, W.; Isbra, W., Direct ethanol metabolites such as ethyl glucuronide (EIG), ethyl sulfate EtS), ethyl phosphate (EtP), fatty acid ethyl esters (FAEEs) and phosphatidyl ethanol (PEth) - When to use, how to use. Alcoholism-Clinical and Experimental Research 2005, 29, (5), 113a-113a. (13) Esteve-Turrillas, F. A.; Bicker, W.; Lammerhofer, M.; Keller, T.; Lindner, W., Determination of ethyl sulfate - a marker for recent ethanol consumption - in 45 (14) Helander, A.; Beck, O., Mass spectrometric identification of ethyl sulfate as an ethanol metabolite in humans. Clinical Chemistry 2004, 50, (5), 936-937. (15) Krivankova, L.; Caslavska, J.; Malaskova, H.; Gebauer, P.; Thormann, W., Analysis of ethyl glucuronide in human serum by capillary electrophoresis with sample self-stacking and indirect detection. Journal of Chromatography A 2005, 1081, (1), 2-8. (16) Schummer, C.; Appenzeller, B. M. R.; Wennig, R., Quantitative determination of ethyl glucuronide in sweat. Therapeutic Drug Monitoring 2008, 30, (4), 536-539. (17) Bergstrom, J.; Helander, A.; Jones, A. W., Ethyl glucuronide concentrations in two successive urinary voids from drinking drivers: relationship to creatinine content and blood and urine ethanol concentrations. Forensic Science International 2003, 133, (1-2), 86-94. (18) Anne, L.; Mitra, S.; Shenoy, V.; Ruzicka, R.; Gines, L.; Seto, N., A high Sensitivity Homogeneous enzyme immunoassay for the detection of ethyl glucuronide in human urine. Clinical Chemistry 2007, 53, (6), A100-A100. (19) Alt, A.; Janda, I.; Seidl, S.; Wurst, F. M., Determination of ethyl glucuronide in hair samples. Alcohol and Alcoholism 2000, 35, (3), 313-314. (20) Junghanns, K.; Graf, I.; Pfluger, J.; Wetterling, G.; Ziems, C.; Ehrenthal, D.; Zollner, M.; Dibbelt, L.; Backhaus, J.; Weinmann, W.; Wurst, F. M., Urinary ethyl glucuronide (EtG) and ethyl sulphate (EtS) assessment: valuable tools to improve verification of abstention in alcohol-dependent patients during in-patient treatment and at follow-ups. Addiction 2009, 104, (6), 921-926. (21) Sachs, H.; Raff, I., Comparison of Quantitative Results of Drugs in Human Hair by Gc/Ms. Forensic Science International 1993, 63, (1-3), 207-216. (22) Schmitt, G.; Aderjan, R.; Keller, T.; Wu, M., Ethyl Glucuronide - an Unusual 46 Ethanol Metabolite in Humans - Synthesis, Analytical Data, and Determination in Serum and Urine. Journal of Analytical Toxicology 1995, 19, (2), 91-94. (23) Bosma, P.J.; Chowdhury, J.R.; Bakker, C.; Gantla, S.; Boer, A. de; Oostra, B.A.; Lindhout, D.; Tytgat, G.N.; Jansen, P.L.; Elferink, R.P. Oude; Chowdhury, N.R., The genetic basis of the reduced expression of bilirubin UDP– glucuronosyltransferase 1 in Gilbert’s syndrome, N. England Journal of Medicine 1995, (333), 1171–1175. (24) Dahl, H.; Stephanson, N.; Beck, O.; Helander, A., Comparison of urinary excretion characteristics of ethanol and ethyl glucuronide. Journal of Analytical Toxicology 2002, 26, (4), 201-204. (25) Goll, M.; Schmitt, G.; Ganssmann, B.; Aderjan, R. E., Excretion profiles of ethyl glucuronide in human urine after internal dilution. Journal of Analytical Toxicology 2002, 26, (5), 262-266. (26) Nalesso, A.; Frison, G.; Favretto, D.; Maietti, S.; Ferrara, S. D., Synthesis and characterization of ethyl sulfate and D-5-ethyl sulfate as reference substances for applications in clinical and forensic toxicology. Rapid Communications in Mass Spectrometry 2005, 19, (23), 3612-3614. (27) Helander, A.; Bottcher, M.; Fehr, C.; Dahmen, N.; Beck, O., Detection Times for Urinary Ethyl Glucuronide and Ethyl Sulfate in Heavy Drinkers during Alcohol Detoxification. Alcohol and Alcoholism 2009, 44, (1), 55-61. (28) Baranowski, S.; Serr, A.; Thierauf, A.; Weinmann, W.; Perdekamp, M. G.; Wurst, F. M.; Halter, C. C., In vitro study of bacterial degradation of ethyl glucuronide and ethyl sulphate. International Journal of Legal Medicine 2008, 122, (5), 389-393. (29) Helander, A.; Dahl, H., Urinary tract infection: A risk factor for false-negative urinary ethyl glucuronide but not ethyl sulfate in the detection of recent alcohol consumptio. Clinical Chemistry 2005, 51, (9), 1728-1730. (30) Halter,C.; Dresen, S.; Lauer, J.; Weinmann, W.; Wurst, F.M., Is ethyl phosphate 47 another marker for ethanol consumption? Alcoholism: Clinical and Experimental Research 2005, (Supplement), (29), 85A. (31) Wurst, F. M.; Wiesbeck, G. A.; Alling, C.; Aradottir, S.; Pragst, F.; Johnson, B.; Javors, M.; Ait-Daoud, N.; Skipper, G. E.; Spies, C.; Nachbar, Y.; Lesch, O.; Ramskogler, K.; Hartmann, S.; Wolfersdorf, M.; Dresen, S.; Weinmann, W., Direct ethanol metabolites such as ethyl glucuronide (EtG), fatty acid ethyl esters (FAEEs), phosphatidyl ethanol (PEth) and ethyl sulphate - A new line of sensitive and specific biomarkers. Alcoholism-Clinical and Experimental Research 2004, 28, (8), 53a-53a. (32) Bicker, W.; Lammerhofer, M.; Keller, T.; Schuhmacher, R.; Krska, R.; Lindner, W., validated method for the determination of the ethanol consumption markers ethyl glucuronide, ethyl phosphate, and ethyl sulfate in human urine by reversed-phase/weak anion exchange liquid chromatography-tandem mass spectrometry. Analytical Chemistry 2006, 78, (16), 5884-5892. (33) Rosano, T. G.; Lin, L., Ethyl Glucuronide Excretion in Humans Following Oral Administration of and Dermal Exposure to Ethanol. Journal of Analytical Toxicology 2008, 32, (8), 594-600. (34) Pragst, F.; Yegles, M., Determination of fatty acid ethyl esters (FAEE) and ethyl glucuronide (EtG) in hair: A promising way for retrospective detection of alcohol abuse during pregnancy? Therapeutic Drug Monitoring 2008, 30, (2), 255-263. (35) Morini, L.; Politi, L.; Groppi, A.; Stramesi, C.; Polettini, A., Determination of ethyl glucuronide in hair samples by liquid chromatography/electrospray tandem mass spectrometry. Journal of Mass Spectrometry 2006, 41, (1), 34-42. (36) Shah, R.; LaCourse, W.R.; An improved method to detect ethyl glucuronide in urine using reversed-phase liquid chromatography and pulsed electrochemical detection, Analytical Chi mica. Acta 2006 (576) , 239–245. (37) Jung, B.; Caslavska, J.; Thormann, W., Determination of ethyl sulfate in human serum and urine by capillary zone electrophoresis. Journal of Chromatography A 2008, 1206, (1), 26-32. 48 (38) Bottcher, M.; Beck, O.; Helander, A., Evaluation of a new immunoassay for urinary ethyl glucuronide testing. Alcohol and Alcoholism 2008, 43, (1), 46-48. (39) Zimmer, H.; Schmitt, G.; Aderjan, R., Preliminary immunochemical test for the determination of ethyl glucuronide in serum and urine: Comparison of screening method results with gas chromatography-mass spectrometry. Journal of Analytical Toxicology 2002, 26, (1), 11-16. (40) Zheng, Y.F.; Helander, A., Solid-phase extraction procedure for ethyl glucuronide in urine. Journal of Analytical Toxicology 2008, 32, (6), 778-781. (41) Janda, I.; Weinmann, W.; Kuehnle, T.; Lahode, M.; Alt, A., Determination of ethyl glucuronide in human hair by SPE and LC-MS/MS. Forensic Science International 2002, 128, (1-2), 59-65. (42) Morini, L.; Marchei, E.; Pellegrini, M.; Groppi, A.; Stramesi, C.; Vagnarelli, F.; Garcia-Algar, O.; Pacifici, R.; Pichini, S., Liquid Chromatography With Tandem Mass Spectrometric Detection for the Measurement of Ethyl Glucuronide and Ethyl Sulfate in Meconium: New Biomarkers of Gestational Ethanol Exposure? Therapeutic Drug Monitoring 2008, 30, (6), 725-732. (43) Freire, I. A.; Barrera, A. M. B.; Silva, P. C.; Duque, M. J. T.; Gomez, P. F.; Eijo, P. L., Microwave assisted extraction for the determination of ethyl glucuronide in urine by gas chromatography-mass spectrometry. Journal of Applied Toxicology 2008, 28, (6), 773-778. (44) Nishikawa, M.; Tsuchihashi, H.; Miki, A.; Katagi, M.; Schmitt, C.; Zimmer, H.; Keller, T.; Aderjan, R., Determination of ethyl glucuronide, a minor metabolite of ethanol, in human serum by liquid chromatography electrospray ionization mass spectrometry. Journal of Chromatography B 1999, 726, (1-2), 105-110. (45) Weinmann, W.; Schaefer,P; Thierauf, A.; Schreiber,A.; Wurst,F.M., Confirmatory analysis of ethylglucuronide in urine by liquid chromato -graphy/electrospray ionization/tandem mass spectrometry according to forensic guidelines, Journal of the American Society for Mass Spectrometry 2004, (15), 49 (46) Politi, L.; Morini, L.; Groppi, A.; Poloni, V.; Pozzi, F.; Polettini, A., Direct determination of the ethanol metabolites ethyl glucuronide and ethyl sulfate in urine by liquid chromatography/electrospray tandem mass spectrometry. Rapid Communications in Mass Spectrometry 2005, 19, (10), 1321-1331. (47) Morini, L.; Politi, L.; Zucchella, A.; Polettini, A., Ethyl glucuronide and ethyl sulphate determination in serum by liquid chromatography-electrospray tandem mass spectrometry. Clinica Chimica Acta 2007, 376, (1-2), 213-219. (48) Stephanson, N.; Dahl, H.; Helander, A.; Beck, O., Direct quantification of ethyl glucuronide in clinical urine samples by liquid chromatography-mass spectrometry. Therapeutic Drug Monitoring 2002, 24, (5), 645-651. (49) You, Y. W.; Uboh, C. E.; Soma, L. R.; Guan, F. Y.; Li, X. Q.; Rudy, J. A.; Chen, J. W., Biomarkers of alcohol abuse in racehorses by liquid chromatography/tandem mass spectrometry. Rapid Communications in Mass Spectrometry 2007, 21, (23), 3785-3794. (50) Rosales-Conrado, N.; Leon-Gonzalez, M. E.; Perez-Arribas, L. V.; Polo-Diez, L. M., Determination of chlorophenoxy acid herbicides and their esters in soil by capillary high performance liquid chromatography with ultraviolet detection, using large volume injection and temperature gradient. Analytica Chimica Acta 2002, 470, (2), 147-154. (51) Guinebault, P.; Broquaire, M., Large-volume injection of samples dissolvedin a non-eluting solvent- application to the determination of antipyrene using normal-phase high-performance liquid chromatography Journal of Chromatography 1981, 217, (NOV), 509-522. (52) Cappiello, A.; Famiglini, G.; Berloni, A., Large volume injection of acidic pesticides by reversed-phase micro high-performance liquid chromatography. Journal of Chromatography A 1997, 768, (2), 215-222. (53) Hennion, M. C.; Pichon, V., Solid-phase extraction of polar organic pollutants 50 from water. Environmental Science and Technology 1994, 28, (13), A576-A583. (54) Silver, M. R.; Trosper, T. D.; Gould, M. R.; Dickinson, J. E.; Desotelle, G. A., The use of large volume injections for the isocratic separation of phenylthiohydantoin amino acids by microbore liquid chromatography. Journal of Liquid Chromatography 1984, 7, 559-568. (55) Mefford, I. N., Chromatographic approaches to signal and selectivity enhancement for determination of biogenic-amines by liquid chromatography with amperometric detection Life Sciences 1987, 41, (7), 893-896. (56) Hogenboom, A. C.; Hofman, M. P.; Kok, S. J.; Niessen, W. M. A.; Brinkman, U. A. T., Determination of pesticides in vegetables using large-volume injection column liquid chromatography-electrospray tandem mass spectrometry. Journal of Chromatography A 2000, 892, (1-2), 379-390. (57) Ingelse, B. A.; van Dam, R. C. J.; Vreeken, R. J.; Mol, H. G. J.; Steijger, O. M., Determination of polar organophosphorus pesticides in aqueous samples by direct injection using liquid chromatography-tandem mass spectrometry. Journal of Chromatography A 2001, 918, (1), 67-78. (58) Hidalgo, C.; Sancho, J. V.; Hernandez, F., Trace determination of triazine herbicides by means of coupled-column liquid chromatography and large volume injection. Analytica Chimica Acta 1997, 338, (3), 223-229. (59) Hutta, M.; Rybár, I.; Chalányová, M., Liquid chromatographic method development for determination of fungicide epoxiconazole enantiomers by achiral and chiral column switching technique in water and soil. Journal of Chromatography A 2002, 959, (1-2), 143-152. (60) Schultz, M. M.; Barofsky, D. F.; Field, J. A., Quantitative determination of fluorinated alkyl substances by large-volume-injection liquid chromatography tandem mass spectrometry-characterization of municipal wastewaters. Environmental Science and Technology 2006, 40, (1), 289-295. (61) Chiaia, A.; Green, C.; Field, J.,Eliminating Solid Phase Extraction with 51 Large-Volume Injection LC/MS/MS: Analysis of Illicit and Legal Drugs and Human Urine Indicators in US Wastewaters, Environment Science Technology, 2008, 42, (23), 8841–8848. (62) Huset, A. A.; Chiaia, A.; Barofsky, D. F.; Jonkers, N.; Kohler, H.-P.; Ort, C.; Giger, W.; Field, J., Occurrence and mass flows of fluorochemicals in the Glatt Valley watershed, Switzerland. Environment Science Technology, 2008 ,42, (17),6369-77. (63) Isaacson, C. W.; Usenko, C. Y.; Tanguay, R. L.; Field, J. A., Quantification of fullerenes by LC/ESI-MS and its application to in vivo toxicity assays. Analytical Chemistry 2007, 79, (23), 9091-9097. (64) Dresen, S.; Weinmann, W.; Wurst, F. M., Forensic confirmatory analysis of ethyl sulfate - A new marker for alcohol consumption - by liquid- chromatography /electrospray ionization/tandem mass spectrometry. Journal of the American Society for Mass Spectrometry 2004, 15, (11), 1644-1648.