Skip to main content
NIHPA Author Manuscripts logoLink to NIHPA Author Manuscripts
. Author manuscript; available in PMC: 2019 Sep 1.
Published in final edited form as: J Chromatogr B Analyt Technol Biomed Life Sci. 2018 Jul 5;1093-1094:119–127. doi: 10.1016/j.jchromb.2018.07.004

Determination of methyl isopropyl hydantoin from rat erythrocytes by gas-chromatography mass-spectrometry to determine methyl isocyanate dose following inhalation exposure

Brian A Logue a,*, Zhiling Zhang a, Erica Manandhar a, Adam L Pay a, Claire R Croutch b, Eric Peters b, William Sosna b, Jacqueline S Rioux c, Livia A Veress c, Carl W White c
PMCID: PMC6218199  NIHMSID: NIHMS1500133  PMID: 30015309

Abstract

Methyl isocyanate (MIC) is an important precursor for industrial synthesis, but it is highly toxic. MIC causes irritation and damage to the eyes, respiratory tract, and skin. While current treatment is limited to supportive care and counteracting symptoms, promising countermeasures are being evaluated. Our work focuses on understanding the inhalation toxicity of MIC to develop effective therapeutic interventions. However, in-vivo inhalation exposure studies are limited by challenges in estimating the actual respiratory dose, due to animal-to-animal variability in breathing rate, depth, etc. Therefore, a method was developed to estimate the inhaled MIC dose based on analysis of an N-terminal valine hemoglobin adduct. The method features a simple sample preparation scheme, including rapid isolation of hemoglobin, hydrolysis of the hemoglobin adduct with immediate conversion to methyl isopropyl hydantoin (MIH), rapid liquid-liquid extraction, and gas-chromatography mass-spectrometry analysis. The method produced a limit of detection of 0.05 mg MIH/kg RBC precipitate with a dynamic range from 0.05–25 mg MIH/kg. The precision, as measured by percent relative standard deviation, was <8.5%, and the accuracy was within 8% of the nominal concentration. The method was used to evaluate a potential correlation between MIH and MIC internal dose and proved promising. If successful, this method may be used to quantify the true internal dose of MIC from inhalation studies to help determine the effectiveness of MIC therapeutics.

Keywords: methyl isocyanate, liquid-liquid extraction, gas-chromatography mass-spectrometry, inhalation exposure

1. Introduction

Methyl isocyanate (MIC) is used for carbamylation of amines as an important precursor for the synthesis of carbamate pesticides and diisocyanates (i.e., intermediates in synthesis of plastics) (13). Although industrially important, MIC is also highly toxic, as tragically demonstrated by Bhopal disaster in 1984, where it is estimated that 8000 or more people died within minutes of exposure to MIC (46). Victims of MIC exposure suffer from severe health effects, both acutely and long-term, with MIC causing irritation and injury to the eyes, respiratory tract, and skin, with most damage occurring to the lungs and airways (79). MIC can enter the body via inhalation or skin contact with the toxicity of MIC stemming from its ability to readily react with electronegative groups in biological molecules (e.g., amino groups). Specifically, MIC mainly carbamoylates end-terminal amino acids of tissue proteins and side-chain amino groups of lysine (2, 10, 11), although about 20 other adducts have also been found (12). MIC-protein and DNA alkylation results in tissue hypoxia and cytotoxicity (1015), targeting various organs, and leading to ophthalmic, respiratory, reproductive, neuromuscular, psychological, neural-behavioral, and other systematic problems (10, 1624).

While current treatment is limited to supportive care and treatment of symptoms, promising drug treatments are being evaluated. New investigations are underway which focus on understanding the inhalation toxicity of MIC to develop effective therapeutic interventions. However, in-vivo inhalation exposure studies are limited by challenges in determining the actual respiratory dose, because the dose depends on many factors other than vapor concentration and exposure time, including respiratory rate, tidal volume, minute volume, and deposition rate within various regions of respiratory tract (25). These parameters are very difficult to estimate in animals, especially during active MIC exposure. Therefore, for inhalation exposures, it is very difficult to quantify how much MIC is internalized (i.e., the “internal dose”) from external parameters. To address this problem, quantification of a known MIC biomarker may allow better estimation of internal dose.

Because of its reactivity, MIC is quickly eliminated from biological systems, mainly via its reaction with protein-based amino groups. Therefore, biomarkers used to verify exposure to MIC are typically based on protein adducts, with the most common based on the reaction of MIC with the N-terminal valine in hemoglobin (Hb) (2, 15, 2629). In fact, the MIC-N-terminal valine adduct has been used to verify exposure of individuals during the Bhopal disaster (15). Detection and quantification of the MIC-N-terminal valine Hb adduct is accomplished by the Scheme shown in Figure 1, featuring acid hydrolysis, cyclization of the resulting N-(methylcarbamoyl)valine, and subsequent extraction of the methyl isopropyl hydantoin (MIH) using liquid-liquid extraction. This process is performed in each of the methods available for the analysis of the MIC-N-terminal hemoglobin adduct listed in Table 1. Although each of these methods are effective, most of the methods are arduous, lengthy, complex, generate a relatively large amount of organic waste, and consume considerable amounts of energy (Table 1). Mráz et al. (28) simplified the typical sample preparation as compared to the other methods in Table 1. Although the method was simplified to 20 steps and approximately 9 hr, it still was lengthy, consumed considerable amounts of energy, and generated a large amount of organic waste. Wang et al. (29) also simplified the sample preparation of MIH from MIC-adducted hemoglobin by using a 96-well protein precipitation and phospholipid removal plate. This method featured similar hydrolysis and MIH formation steps as the other methods in Table 1, but instead of liquid-liquid extraction (LLE), a sorbent plate was used to isolate the MIH for UHPLC-MS-MS analysis. While this method was rapid, it still necessitated many steps (i.e., 18) and specialized equipment for the sample preparation.

Figure 1.

Figure 1.

Reaction of methyl isocyanate with the N-terminal valine of hemoglobin to produce a carbamoylated hemoglobin. The carbamoylated hemoglobin is hydrolyzed by Edman degradation to form N-(methylcarbamoyl)valine which cyclizes under acidic conditions to form MIH for subsequent analysis. Structures from electron ionization fragmentation and the resulting mass spectrum are also shown. Asterisks denote the locations of the stable isotopes in the internal standard for each of the fragments.

Table 1.

Comparison of methods of analysis for methyl isopropyl hydantoin produced from Edman degradation of carbamylation of the N-terminal valine of hemoglobin.

Reference Year Analytical
Method
LOD Approximate
Estimated Time
(hr)
Steps
Ramachandran et al. (15) 1988 EI-GC-FID 0.0094 mg/L lysateb 20c 22
Venkateswaran et al. (30)a 1992 HPLC-DAD (200 nm) 0.016 mg/L lysateb 20c 22
Angerer et al. (26)a 1998 EI-GC-MS 0.30 mg/kg 20c 22
Mráz et al. (28) 2002 EI-GC-MS 0.031 mg/kg 9 20
Mráz et al. (31)e 2006 EI-GC-NPD 0.16 mg/kg 9 20
Käfferlein et al. (27) 2009 EI-GC-MS 0.078 mg/kg 60d >37
Wang et al. (29) 2014 UHPLC-MS-MS 1.6 mg/kg 7,19c 18
a

Same sample preparation as Ramachandran et al. (15).

b

Did not report the amount of red blood cell precipitate mass per mL of lysate.

c

Includes an overnight drying step.

d

Includes two overnight steps.

e

Same sample preparation as Mráz et al. (28).

The objective of the current study was to develop a more rapid, simpler, and greener method than currently available for evaluation of MIC exposure via analysis of MIH following hydrolysis of carbamylated N-terminal valine of hemoglobin. A secondary objective was to evaluate the potential of the method to estimate the internalized dose of MIC from inhalation exposures.

2. Experimental

2.1. Reagents and standards

All reagents were at least HPLC grade unless otherwise noted. Methanol, hydrochloric acid (certified ACS), acetic acid (certified ACS), acetone, ethyl acetate, sodium hydroxide (certified ACS) and sodium bicarbonate (certified ACS) were purchased from Fisher Scientific (Fair Lawn, NJ, USA). Reverse-osmosis water was purified to 18.2 MΩ-cm using a Lab Pro polishing from Labconco (Kansas City, KS, USA). Methyl isocyanate (MIC) was synthesized for the analytical work in our lab by the method of Kaushik et al. (32) based on the Curtius Rearrangement method, which involved refluxing acetyl chloride with sodium azide in toluene until all starting materials were consumed. The MIC was collected via distillation. Purity was confirmed using 1H-NMR and at 95%. MIC for the animal exposures was prepared at MRIGlobal (Kansas City, MO) by the same general procedure. The MIC prepared at MRIGlobal was 99.2% pure, as verified by gas chromatography-flame ionization detection. Methyl isopropyl hydantoin (MIH) was synthesized in our lab according to Ramachandran et al. (15) by the reaction of MIC with L-valine in acidic solution. MIH purity was verified by 1H-NMR and GC-MS analysis and was 97% pure. The internal standard, MIH-13C5 15N, was synthesized by the same procedure using valine-13C515N, purchased from Sigma Aldrich (St. Louis, MO). MIH-13C5 15N purity was verified by 1H-NMR and GC-MS as 99.8% pure. MIH and internal standard stock solutions (1 g/mL) were prepared and stored in a −30 °C freezer. For each experiment, they were brought to room temperature by leaving them on bench top and were diluted to the desired concentration.

2.2. Biological fluids

For method development and validation, Sprague-Dawley rat red blood cells (RBCs) with K2EDTA as anticoagulant, were purchased from Bioreclamation IVT (Westbury, NY, USA) and immediately stored at −80 °C until used.

RBCs from MIC-exposed male Sprague-Dawley rats were received from MRIGlobal (Kansas City, MO) with all procedures performed according to approved Institutional Animal Care and Use Committee protocols there. Male Sprague-Dawley rats (250–300 g) were obtained from Charles River (Kingston, NY). Animals were acclimated to laboratory conditions for 5–7 days prior to study, including acclimation to nose-only exposure chambers at variable time intervals for 72 hours before study. Food and water were provided ad libitum. A nose-only (CH Technologies; Westwood, NJ) inhalation system was used for the exposure of rats with the entire inhalation system placed in a fume hood. A proprietary custom vapor diffusion system (MRIGlobal) was used to generate MIC vapor. Rats were acclimated to the exposure system for three sequential days prior to MIC exposure. The vapor was then delivered to the plenum of the exposure system in a mixture of dry nitrogen (50 mL/min ultra-high purity nitrogen) that was then blended with high efficiency particulate air (HEPA)-carbon-filtered dry air (10–15 L/min, depending on the desired concentration). Downstream from the site of mixing and prior to the plenum, gas constituents were monitored by Fourier transform infrared spectroscopy by accessing the system via a 3-way valve. Exhaust from the system was scrubbed in 10% NaOH and delivered to the fume hood. Conscious rats were exposed for 30 min, followed by in-cage recovery for 1, 2, 4, or 8 hr. Blood samples were collected just prior to euthanasia (under ketamine/xylazine anesthesia), by placement of a butterfly catheter in the descending abdominal aorta of each rat. Blood (5 mL) was collected into a pre-citrated 5-mL syringe (0.5 mL of 3.2% sodium citrate) and transferred to a centrifuge tube. Citrated blood was centrifuged at 750 rpm for 15 minutes at 2–8 °C. The blood was again centrifuged at 3600 rpm for an additional 10 minutes at 2–8 °C. Plasma was removed, and the remaining red blood cells were frozen and stored at −80 °C until shipment. The RBCs were shipped on dry ice to South Dakota State University where they were stored at −80 °C until ready for analysis.

2.3. Sample preparation

RBCs (3 mL) were added to a 15-mL centrifuge tube. (Note: Although 3 mL of RBC lysate was used to produce enough protein for triplicate analysis, only 700–800 µL of RBC lysate was typically necessary to provide 200 mg of protein.) Acetone with 1% HCl (v/v), was added to the RBCs with a 3:1 volume ratio of acetone to RBC. The mixture was vortexed, and then centrifuged at 800 x g for 10 mins at 20 °C. The supernatant was discarded. The precipitate was washed once by adding 6 mL of acetone and breaking the pellet with a clean spatula. The mixture was again centrifuged, as above, and the supernatant was discarded. The precipitate was dried in a centrifugal evaporator (Labconco, Kansas City, USA) equipped with a rotary vacuum pump (Edwards, Glenwillow, USA) at 30 °C until dry. If not analyzed immediately, the precipitate was stored at −80 °C until ready for use. If the precipitate was stored at −80 °C, it was thawed, unassisted, at room temperature prior to continuing sample preparation.

A portion of the precipitate (200 mg) was added to a clean 15 mL centrifuge tube. A mixture of 1:1 (v/v) hydrochloric acid and acetic acid (1.5 mL total volume) was added to the precipitate to produce MIH from MIC-adducted protein. The centrifuge tube was capped and heated at 110 °C for 1.3 hours. The sample was then removed from heat and cooled to room temperature. Aqueous NaOH (1.4 mL of 10 M) was added to neutralize the acids. Prior to finalizing the method, multiple combinations of NaOH concentration and volume were tested for their ability to adjust the pH of the solution to 3–5 and 1.4 mL of 10 M NaOH was found to consistently produce the desired pH. After pH adjustment, ethyl acetate (1.5 mL) was added to the vial to extract the MIH. The sample was capped and shaken vigorously for 1.5 minutes, then left on the bench top for 15 mins. The sample was centrifuged at 2000 x g for 5 mins and the upper organic layer was transferred to a new 15-mL centrifuge tube. The ethyl acetate was washed by adding 2.5 mL of 1 M aqueous NaHCO3 to neutralize residual base in the ethyl acetate. Following addition of NaHCO3, the vial was shaken for 1.5 mins, stored at room temperature for 15 mins, and centrifuged at 2000 x g for 5 mins. An aliquot of the organic layer (approximately 1 mL) was then transferred to a 2 mL GC vial and the vial was capped with a Teflon-coated septa screw-cap prior to GCMS analysis.

2.4. GC–MS analysis of MIH

The extracted MIH was analyzed using an Agilent GC–MS system equipped with a 6890N gas chromatograph and a 5975B inert XL electron ionization (EI)/chemical ionization (CI) mass selective detector. The sample (1 μL) was injected into a heated injection port at 250 °C in splitless mode, and two minutes after injection, the split vent was opened at a flow rate of 50 mL/min. The compound was ionized using EI at 70 eV. A DB-5MS bonded phase column (30 m x 0.25 mm I.D., 0.25 m film thickness; J & W Scientific, Santa Clara, CA) was used. Hydrogen, produced by a hydrogen generator (Parker Manufacturing LTD; Gateshead, United Kindom), was used as the carrier gas at a flow rate of 1.5 mL/min. The initial oven temperature was set at 70 °C for 1 min, and then increased at 50 °C/min to 150 °C and held for 1 minute. The temperature was then increased to 180 °C at 20 °C/min, and finally increased to 250 °C at 100 °C/min and held for 3 mins. The temperatures of the MS transfer line, the source, and the quadrupole were 250, 230, and 150 °C, respectively. Selected ion mode (SIM) was used to quantify MIH for the fragments shown in Figure 1 using 114 m/z ([C4H6N2O2]+, quantification) and 156 m/z (C7H12N2O2·]+, identification). The ions monitored for the internal standard were m/z ([12C213C2H614N15NO2]+, quantification) and 162 m/z ([13C512C2H1214N15NO2·]+, identification). Each ion was monitored with a dwell time of 100 ms and the solvent delay was 2.85 minutes.

2.5. Calibration, quantification, and limit of detection

Validation of the method was performed by generally following Food and Drug Administration guidelines (3335). To determine the limit of detection (LOD), MIH stock solution (1 g/L) was diluted in water to create standards of 0.02, 0.05, 0.1, 0.2, 0.5, 1, 10, and 100 mg/L. A standard solution was spiked (50 μL) into a vial with 200 mg RBC precipitate prepared from rats which were not exposed to MIC. The spiked rat RBC precipitate was then prepared as described above via acid hydrolysis and extraction with ethyl acetate. The extracted MIH was then analyzed via GCMS. The lowest MIH concentration that reproducibly produced a signal-to-noise ratio of 3 was defined as the LOD for MIH. Noise was measured by averaging the peak-to-peak noise in prepared, unspiked RBC samples over the retention time of the analyte.

After the LOD was determined, the calibration curve dynamic range was established. For the calibrators, rat RBC precipitate (200 mg) was spiked with 100 μL of a mixture of MIH internal standard (50 μL, 10 mg/L) and MIH (50 μL) at concentrations ranging from the 0.05 to 25 mg/kg RBC precipitiate. Each sample was prepared in triplicate. The average peak area ratios of MIH to IS were plotted as a function of MIH concentration to determine the linearity, accuracy, and precision of the calibration. Peak areas were calculated by manual integration from baseline to baseline. The accuracy was quantified as the ratio of the back-calculated concentration to the nominal concentration for all calibration standards. The lower limit of quantification (LLOQ) and upper limit of quantification (ULOQ) were selected as the lowest and highest concentrations with less than 15% relative standard deviation (as a measure of precision) and with 100 ± 15% accuracy.

After the linear dynamic range was established, the accuracy and precision of the method was evaluated over three days (within 10 calendar days). Calibration standards within the linear dynamic range were created in triplicate and QC standards of 0.188 mg/kg (low QC), 1.88 mg/kg (medium QC), and 8.75 mg/kg (high QC) were prepared in quintuplicate. Calibration curves were created each day and used to calculate the concentration of each QC standard. QCs were not used as part of the calibration curve. The intraassay (within same day) and interassay (over three separate days) accuracy and precision for the developed method were determined from the QCs.

2.6. Selectivity and stability

The ability to differentiate and quantify MIH in the presence of other RBC protein components following sample preparation (assay selectivity) was determined by comparing unspiked and MIH-spiked blood RBC proteins. The absence of signals above the baseline of the blank over the elution time of MIH was indicative of high selectivity. Resolution of the MIH peak was also calculated as a measure of selectivity by standard methods (36).

To evaluate the stability of MIH or hemoglobin-MIC adducts (Hb-MIC) over the short and long-term, the following experiments were performed: auto-sampler stability, bench top stability, and long-term stability at −80 °C. Auto-sampler stability was carried out by spiking RBC precipitate with MIH and preparing for analysis. The samples were placed on the auto-sampler (at ambient temperature) and analyzed at approximately 0, 1.3, 2.6, 5, 15, and 24 h following preparation. Internal standard was not used for the auto-sampler stability experiment, as it would correct for the loss of MIH during the storage.

The benchtop stability of the MIC-protein adduct was evaluated by initially spiking MIC in RBCs at levels which produced MIH signals generally equivalent to the low and high QCs: 1.61 µmol/g and 80.9 µmol/g, respectively. The MIC-spiked rat RBC samples were vortexed for 1 min and shaken overnight in a Benchmark INCU-SHAKER™ 10-L Shaking Incubator at 290 rpm and room temperature. The samples were then stored on the bench top for 0, 2, 5, 12, and 24 hours. They were then precipitated, dried, and stored in −80 °C freezer until all the protein samples were ready for analysis. Prior to analysis, the samples were removed from the freezer and allowed to reach room temperature. The remaining sample preparation and analysis steps described above were then completed. The experiment for the long-term stability of the MIC-protein adduct was similar to the bench-top stability experiment, except MIC-spiked RBCs were stored at −80 °C and 4 °C for 0, 1, 2, 5, 15, and 30 days before they were prepared using the developed method.

2.7. Recovery and matrix effect

To determine the recovery of MIH, a set of samples were prepared in ethyl acetate which contained the amount of MIH representative of 100% recovery. Specifically, triplicates of low, medium, and high QC concentrations in MeOH (50 µL) were dried in air, then 1.5 mL ethyl acetate was added and vortexed to dissolve the MIH prior to GCMS analysis. These samples were analyzed alongside a set of low, medium, and high MIH QCs prepared in rat RBC precipitate prepared by the current method. Following GCMS analysis, the recovery (i.e., signal recovery) for each QC was quantified as the average percentage of the peak areas of the MIH-spiked RBC samples to that of the corresponding MIH QCs in ethyl acetate. It is important to note that the recovered signal obtained in this manner is influenced by both matrix effects and recovery.

To evaluate the matrix effect of the RBC precipitate on the analysis of MIH, calibration curves of MIH in both aqueous solution and RBC-precipitate were established. The samples were prepared using the identical procedures as described above, except the MIH and MIH internal standard were added directly to the acetic acid:HCl mixture with no RBC precipitate for the non-matrix calibration standards. The ratio of the slopes of the calibration curves in RBC-precipitate compared to the slope obtained for aqueous calibration standards was used to quantify the matrix effect.

3. Results and discussion

3.1. GC–MS analysis of MIH

The method presented here shortens the time needed for analyzing MIC exposed RBCs from ≥7 hours and over ≥18 steps for the methods listed in Table 1 to 4–5 hours and 14 steps. The steps associated with the Käfferlein et al. (27) method are shown in Figure 2 for comparison with the method presented here (Figure 3). Both the Käfferlein et al. (27) method and the method presented here were conducted for the same samples in our lab and the analytical parameters achieved for the current method were comparable, but our method was much more rapid, simpler, and greener.

Figure 2.

Figure 2.

Schematic representation of the sample preparation procedure of the Käfferlein et al. (27) method. This method takes at least two days and over 37 steps to prepare blood for analysis of MIH from MIC-adducted hemoglobin. EA – Ethyl Acetate.

Figure 3.

Figure 3.

Schematic representation of the sample preparation procedure used for the current study. This method takes at about 4–5 hours and 14 steps to prepare blood for analysis of MIH from MIC-adducted hemoglobin.

The main highlights of the current method and most methods listed in Table 1 (15, 2628)are the same. RBCs are precipitated and hydrolyzed via treatment with strong acid to produce MIH from MIC adducted N-terminal valine. LLE with ethyl acetate is then used to extract the MIH from the aqueous solution. The extract is then analyzed by GC-FID (15), GC-NPD (31), GC-MS (2628), HPLC-Diode Array Detector (DAD) (30), or UHPLC-MS-MS (29). Although the major features are the same, there are many differences in the current method that simplify the analysis of MIH. First, during precipitation, both protein and cell debris are simultaneously precipitated, whereas in most other methods, cell debris is precipitated first, then proteins in the supernatant are precipitated. The simplification of this process did not affect the precision and accuracy of the current method, but greatly reduced the preparation time and effort. After the RBC precipitate is dried and weighed, it is hydrolyzed by a mixture of HCl and acetic acid. This resulting solution is highly acidic. Some methods prepare this solution via several lengthy steps, including addition of NaOH to adjust the pH to 7, addition of saturated NaCl, and adjustment of the pH to 3–5 using HCl. In the simplified method, the pH of the solution was adjusted to 3 to 5 directly by adding a constant volume of 10 M aqueous NaOH to each sample. In the Käfferlein et al. (27) method, the solution was extracted twice using ethyl acetate (4 mL each), with the solvent subsequently evaporated to approximately 3 mL. In the simplified method, the neutralization and extraction of the hydrolyzed solution were accomplished in one step by adding NaOH and ethyl acetate to the vial at the same time, with no subsequent drying step. For the previous and the current method, the organic phase was further neutralized with sodium bicarbonate before GCMS analysis. Most previous methods further centrifuged the resulting solution, transferred the supernatant to a clean vial, and evaporated it to dryness using nitrogen gas. The residue was then dissolved in ethyl acetate (1 mL) for GCMS analysis.

As outlined above, the current method does not include drying, which greatly reduces the analysis time, energy use, and waste since ethyl acetate has a relatively high boiling point. The omission of the drying step did not significantly affect the precision, accuracy, or sensitivity (LOD) of the current method. In addition to reducing the time and complexity of the analysis, the current method produces less chemical waste than most other methods. For example, the chemicals needed for the Käfferlein et al. (27) method were 2-propanol, ethanol, ethyl acetate, acetic acid, n-hexane, sodium chloride, sodium hydroxide, sodium bicarbonate, and HCl (10 total). The simplified method requires six (acetone, ethyl acetate, acetic acid, sodium hydroxide, sodium bicarbonate, and HCl) and eliminates the most toxic organic chemical used, n-hexane. Furthermore, the amount of chemical waste is drastically reduced by both eliminating the requirement for solvent drying and reducing the extraction and washing steps necessary.

For the current method, the isolated MIH was analyzed via GCMS to produce the chromatograms represented in Figure 4, with MIH eluting at approximately 4.18 min. The method produced adequate peak shape, although the MIH peak tailed slightly (i.e., the peak asymmetry factor, As, was 2.18). The selectivity was good, although there was a small peak at approximately 4.2 min in the non-MIC-exposed rat RBCs, likely due to endogenous N-methylcarbamoylated valine (3739). The closest consistent peak eluted at about 4.4 min, producing a resolution (Rs) of 3.56.

Figure 4.

Figure 4.

SIM mode GCMS chromatograms with selected m/z of 114 of MIH produced via Edman degradation from MIC spiked rat RBCs, RBCs from rats exposed to MIC, MIH spiked rat RBCs, and the non-MIC exposed rat RBCs.

3.2. Endogenous MIH

Endogenous levels of N-methyl carbamoylated N-termal valine residues in Hb are known to be present (3739). Therefore, in order to assess potential interference from MIH not associated with MIC exposure, RBCs from different animals (rabbit, swine, and rat) were evaluated for MIH produced during sample preparation. The MIH produced in the animals evaluated followed the trend: rabbit RBCs >> swine RBCs > rat RBCs. Although the MIH produced from swine RBCs was much less than that from rabbit RBCs, it was still significant enough to affect determination of low concentrations of MIH. Therefore, rat RBC was chosen as the matrix to validate the developed method.

3.3. LOD, dynamic range, and sensitivity

Following method optimization, the LOD of MIH was evaluated at a S/N of 3. The LOD was 0.05 mg/kg RBC precipitate), which compared favorably to the other methods listed in Table 1, only being higher than the Mráz et al. (28) method. There was a small rise in baseline around the retention time of MIH for the naïve samples, which was likely due to endogenous carbamoylation of the N-terminal valine, but even considering this as part of the noise, the LOD was still excellent. Following the determination of the LOD, the calibration curve of MIH was established between 0.05 and 25 mg/kg RBC precipitate. The calibration curve was determined using a 1/x2 weighted fit of the data (the ratio of the peak area of MIH to MIH IS versus the calibration standard concentration). The R2 was 0.993, and residual analysis indicated that the linearity was acceptable with no obvious concentration bias. The true ULOQ was not determined since the calibration curve was linear up to the highest concentration tested. This method produced a large dynamic range of almost 3 orders of magnitude for measuring MIH, which is typically considered excellent for analysis of biological samples (4042).

The sensitivity and calibration repeatability were evaluated over three separate days. The results are shown in Table 2. Each of the three calibration curves produced an R2 > 0.999 and residual analysis indicated no consistent bias in the calibration curves for the 3 days. Although the linearity was consistently excellent, the slopes for each day were not consistent. Therefore, calibration curves should be created for each day of analysis. Evaluation of the peak shape and sensitivity of the method over several months for MIH showed no deleterious effects of multiple injections of the final sample solution.

Table 2.

Calibration equations and coefficients of determination (R2) for calibration curves created over 3 days.

Day Equation R2
1 y = 0.09679x + 0.006831 1
2 y = 0.08767x + 0.01078 0.9996
3 y = 0.08252x + 0.008578 0.9999

3.3. Accuracy and precision

The accuracy and precision of the method were estimated by analysis of quintuplicate low, medium and high QCs on three different days (within a 10-day period) and are summarized in Table 3. The intraassay accuracy and precision were 100 ± 8.0% and <8.1% RSD, respectively. The interassay accuracy and precision were 100 ± 5.7% and <4.5% RSD, respectively. Evaluation of the aggregate data according to Krouwer and Rabinowitz (43) indicates that the within run precision is 6.4, 4.6, and 3.4% RSD for the low, medium and high QC standards, respectively, with total %RSDs, for the method, of 6.8, 5.4, and 3.7% RSD for the low medium and high QC standards, respectively. These values indicate the precision and accuracy of the method are excellent and are well within the FDA method validation guidelines (35). Although most methods from Table 1 do not report accuracy and precision, Mráz et al. (28) reported a precision between 4.1–7.3% for intraassay precision and approximately 10% for intraassay precision. Mráz et al. (28) did not report accuracy since they did not utilize spiked MIH to simulate the “true” concentration as we did here. Käfferlein et al. (27) reported slightly worse precision than the current method: intraassay precision of 4.4–14.2% and interassay precision of 4.9–8.9%. They also reported an accuracy of 100±7%, which is very similar to the current method.

Table 3.

Intra and interassay accuracy and precision of MIH produced by acid hydrolysis of an MIC-protein adduct.

Concentration (mg/kg) Intraassay (within run) Interassay (between run)
Accuracy (%)a Precision (%RSD)a Accuracy (%)b Precision (%RSD)c
Day 1 Day 2 Day 3 Day 1 Day 2 Day 3
0.188 100±1.8 100±3.9 100±2.1 3.6 6.3 8.1 100±2.6 2.3
1.88 100±7.1 100±1.4 100±0.9 5.3 4.9 3.1 100±3.1 2.9
8.75 100±8.0 100±4.1 100±5.1 3.7 2.3 3.9 100±5.7 1.4
a

QC method validation (N = 5).

b

Mean of three different days of QC method validation (N = 15).

c

Between run precision was calculated based on Krouwer and Rabinowitz (43) (N = 15).

3.4. Matrix effects and recovery

To evaluate the effect of the RBC matrix on the analysis of MIH, calibration curves of MIH in both aqueous solution and RBC matrix were compared. The slope of the calibration curve for the samples in RBC matrix was higher than that for the aqueous samples (15800 kg/mg versus 10700 kg/mg, respectively). Because this behavior is unusual for biological matrices, the experiment was repeated, and the results were confirmed. Moreover, the experiment was repeated by spiking extracted RBC matrix with MIH and measuring the slope of the calibration curve. The calibration curve slope in RBC matrix was (20600 kg/mg). The enhancement due to the matrix may be due to a “salting out” effect when the RBC protein precipitate is hydrolyzed, creating a large amount of charged amino acids and peptides (44, 45). Since the method presented does not include the addition of NaCl, as with the Käfferlein et al. (27) method, the hydrolyzed RBC proteins may increase the extraction efficiency of the ethyl acetate for MIH as compared to the aqueous solution by salting out the MIH. It is not clear as to why spiking the MIH prior to sample preparation and following sample preparation produces a difference in the slope, but it is clear that the matrix increases the signal of MIH for this method.

The recoveries for low, medium and high QCs were 88%, 96%, and 98%, respectively. The recovery was excellent for the mid and high QCs, and relatively high for the low QC, although each was below 100%. The loss of MIH during the sample preparation steps is likely due to incomplete extraction of MIH from the blood matrix into the ethyl acetate. This is corroborated, at least partially, by the increase in slope for the RBC matrix during the matrix effect experiment. Comparing to other methods reporting recovery, Ramachandran et al. (15) and Käfferlein et al. (27) reported a recovery of 91% and >93%, respectively. Therefore, the recovery of the current method is comparable to previous methods.

3.5. MIH and MIC protein adduct storage stability.

To determine the stability of the prepared samples on an auto-sampler, LQC and HQC standards were prepared and spiked into rat RBC precipitate (50 μL to 200 mg) along with 50 μL of 10 mg/L MIH IS solution. After the samples went through the sample preparation procedure, they were placed on the auto-sampler and were analyzed at 0, 1.3, 2.6, 5, 15, and 24 hours. The MIH signals were stable for the tested period of 24 hours. The MIH internal standard also corrected for raw signal instability.

We also tested the stability of the N-methyl carbamoylated hemoglobin by spiking MIC directly onto isolated hemoglobin, incubating, washing, and drying the protein. Analysis of MIH following storage on the bench top for different time periods up to 30 days showed that the adduct was stable for all time periods tested. Mráz et al. (28) also tested the stability of the adduct in blood and after isolation of the globin and found similar results, in that the adduct was stable for all conditions tested (i.e., up to 21 days in blood, and up to 2 years as an Hb adduct when stored at 4 °C).

3.6. Evaluation of MIH correlation with MIC exposure

Correlation of MIH to MIC exposure was first evaluated by spiking multiple concentrations of MIC onto hemoglobin and incubating for 24 hours. The resulting hemoglobin was analyzed for MIH. The MIH signal correlated linearly with MIC exposure over the concentration range of 0.08–4.1 mmol (Figure 5) but was generally constant over the concentration range of 1.6–82 µmol. This is likely due to the use of rabbit RBCs producing a large and consistent endogenous MIH concentration.

Figure 5.

Figure 5.

MIH signal as a function of spiked MIC concentration in rabbit RBCs. The error bars represent standard deviation. Note that a higher concentration of internal standard was used with this experiment than used for the final method.

The MIH was then analyzed for multiple exposure concentrations of MIC (125, 250, and 500 ppm) for rats (N = 3 at each concentration). Although the actual dose of MIC cannot be definitively measured, the relationship shown in Figure 6 is very promising for the potential to use MIH to document exposure and to estimate MIC internal dose. More animals and MIC concentrations must be evaluated to gain a true understanding of the correlation between MIH produced and MIC exposure, but the correlations derived from Figures 5 and 6 show the potential of this analytical technique to determine the inhalation exposure of individual animals to MIC.

Figure 6.

Figure 6.

Correlation of MIH concentration with MIC concentration during an inhalation exposure in ppm. The error bars represent standard error of the mean for the analysis of MIH isolated from rat hemoglobin for each exposure group (N = 3 for each dose).

Conclusion

A rapid, greener, and simpler GC-MS method for analysis of MIH isolated from N-methyl carbamoylated hemoglobin was developed and validated. This method is promising for quantifying the internal dose of MIC from inhalation studies. The availability of this method may allow better estimation of the relative exposure level and/or MIC internal dose than external parameters, such as tidal volume, minute volume, and concentration of MIC in the exposure system.

Acknowledgements

We gratefully acknowledge support from the CounterACT Program, National Institutes of Health Office of the Director, and the National Institute of Environmental Health Sciences (NIEHS), Grant number U54 ES027698 (CWW). The opinions or assertions contained herein are the private views of the authors and are not to be construed as official or as reflecting the views of the National Institutes of Health or the CounterACT Program.

Footnotes

Publisher's Disclaimer: This is a PDF file of an unedited manuscript that has been accepted for publication. As a service to our customers we are providing this early version of the manuscript. The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final citable form. Please note that during the production process errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain.

References

  • 1.Kulkarni G, Naik R, Tandel S, Rajappa S. Contra-thermodynamic trans-esteripication of carbamates by counter-attack strategy: A viable non-phosgene, non-mic route to carbamate pesticides. Tetrahedron 1991;47(7):1249–56. [Google Scholar]
  • 2.Mraz J, Šimek P, Chvalova D, Nohova H, Šmigolová P. Studies on the methyl isocyanate adducts with globin. Chemico-biological interactions 2004;148(1–2):1–10. [DOI] [PubMed] [Google Scholar]
  • 3.Senthilkumar CS, Sah NK, Ganesh N. Methyl isocyanate and carcinogenesis: bridgeable gaps in scientific knowledge. Asian Pacific Journal of Cancer Prevention 2012;13(6):2429–35. [DOI] [PubMed] [Google Scholar]
  • 4.Varma R, Varma DR. The Bhopal disaster of 1984. Bulletin of Science, Technology & Society 2005;25(1):37–45. [Google Scholar]
  • 5.Broughton E The Bhopal disaster and its aftermath: a review. Environmental Health 2005;4(1):6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 6.Gupta P Pesticide exposure—Indian scene. Toxicology 2004;198(1–3):83–90. [DOI] [PubMed] [Google Scholar]
  • 7.Kamat S, Patel M, Pradhan P, Taskar SP, Vaidya PR, Kolhatkar V, et al. Sequential respiratory, psychologic, and immunologic studies in relation to methyl isocyanate exposure over two years with model development. Environmental health perspectives 1992;97:241. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8.Andersson N, Muir MK, Mehra V, Salmon A. Exposure and response to methyl isocyanate: results of a community based survey in Bhopal. Occupational and Environmental Medicine 1988;45(7):469–75. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9.Varma DF, Mulay S. The Bhopal accident and methyl isocyanate toxicity. Toxicology of Organophosphate & Carbamate Compounds: Elsevier; 2006. p. 79–88.
  • 10.Shrivastava R Bhopal gas disaster: Review on health effects of methyl isocyanate. Research Journal of Environmental Sciences 2011;5(2):150. [Google Scholar]
  • 11.Sriramachari S The Bhopal gas tragedy: An environmental disaster. Current Science 2004;86(7):905–20. [Google Scholar]
  • 12.Segal A, Solomon JJ, Li F. Isolation of methylcarbamoyl-adducts of adenine and cytosine following in vitro reaction of methyl isocyanate with calf thymus DNA. Chemico-biological interactions 1989;69(4):359–72. [DOI] [PubMed] [Google Scholar]
  • 13.Baumann RP, Seow HA, Shyam K, Penketh PG, Sartorelli AC. The antineoplastic efficacy of the prodrug CloretazineTM is produced by the synergistic interaction of carbamoylating and alkylating products of its activation. Oncology Research Featuring Preclinical and Clinical Cancer Therapeutics 2005;15(6):313–25. [DOI] [PubMed] [Google Scholar]
  • 14.Beyerbach A, Farmer PB, Sabbioni G. Biomarkers for isocyanate exposure: Synthesis of isocyanate DNA adducts. Chemical research in toxicology 2006;19(12):1611–8. [DOI] [PubMed] [Google Scholar]
  • 15.Ramachandran P, Gandhe B, Venkateswaran K, Kaushik M, Vijayaraghavan R, Agarwal G, et al. Gas chromatographic studies of the carbamylation of haemoglobin by methyl isocyanate in rats and rabbits. Journal of Chromatography B: Biomedical Sciences and Applications 1988;426:239–47. [DOI] [PubMed] [Google Scholar]
  • 16.Gupta M, Prabha V. Changes in brain and plasma amino acids of mice intoxicated with methyl isocyanate. Journal of Applied Toxicology 1996;16(6):469–73. [DOI] [PubMed] [Google Scholar]
  • 17.Kennedy AL, Singh G, Alarie Y, Brown WE. Autoradiographic analyses of guinea pig airway tissues following inhalation exposure to 14C-labeled methyl isocyanate. Toxicological Sciences 1993;20(1):57–67. [DOI] [PubMed] [Google Scholar]
  • 18.Kumar S, Kumar P, Seih R, Dwivedi R, Ray P. Effect of exposure to toxic gas on the population of Bhopal: Part I-Epidemiological, clinical, radiological & behavioral studies. Indian journal of experimental biology 1988;26:149–60. [PubMed] [Google Scholar]
  • 19.Mishra P, Samarth R, Pathak N, Jain S, Banerjee S, Maudar K. Bhopal gas tragedy: review of clinical and experimental findings after 25 years. International journal of occupational medicine and environmental health 2009;22(3):193–202. [DOI] [PubMed] [Google Scholar]
  • 20.Rastogi S, Gupta B, Husain T, Kumar A, Chandra S, Ray P. Effect of exposure to toxic gas on the population of Bhopal: Part II--Respiratory impairment. Indian journal of experimental biology 1988;26(3):161–4. [PubMed] [Google Scholar]
  • 21.Salmon A, Muir MK, Andersson N. Acute toxicity of methyl isocyanate: a preliminary study of the dose response for eye and other effects. Occupational and Environmental Medicine 1985;42(12):795–8. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.Saxena A, Singh K, Nagle S, Gupta B, Ray P, Srivastav R, et al. Effect of exposure to toxic gas on the population of Bhopal: Part IV--Immunological and chromosomal studies. Indian journal of experimental biology 1988;26(3):173–6. [PubMed] [Google Scholar]
  • 23.Sharma V, Rao G, Jadhav R, Chandra H, Sriramachari S. High-performance liquid chromatographic estimation of carbamylated amino acids. Current Science 1990:528–9.
  • 24.Tice RR, Luke CA, Shelby MD. Methyl isocyanate: an evaluation of in vivo cytogenetic activity. Environmental and Molecular Mutagenesis 1987;9(1):37–58. [DOI] [PubMed] [Google Scholar]
  • 25.Pauluhn J, Mohr U. Inhalation studies in laboratory animals—current concepts and alternatives. Toxicologic pathology 2000;28(5):734–53. [DOI] [PubMed] [Google Scholar]
  • 26.Angerer J, GoÈen T, KraÈmer A, Käfferlein HU. N-methylcarbamoyl adducts at the N-terminal valine of globin in workers exposed to N, N-dimethylformamide. Archives of toxicology 1998;72(5):309–13. [DOI] [PubMed] [Google Scholar]
  • 27.Käfferlein H, Angerer J, Leng G, Gries W. The MAK-Collection for Occupational Health and Safety: Wiley-VCH; 2009. [Google Scholar]
  • 28.Mráz J, Dušková Š, Gálová E, Nohová H, Krausová P, Linhart I, et al. Improved gas chromatographic–mass spectrometric determination of the N-methylcarbamoyl adduct at the N-terminal valine of globin, a metabolic product of the solvent N, N-dimethylformamide. Journal of Chromatography B 2002;778(1–2):357–65. [DOI] [PubMed] [Google Scholar]
  • 29.Wang C-M, Liu Q, Li J, Xu B, Mi K, Cheng J. Rapid Determination of N-Methylcarbamoyl Adduct in Hemoglobin of Workers Exposed to N,N-Dimethylformamide by Ultra High Performance Liquid Chromatography-Mass Spectrometry. Chinese Journal of Analytical Chemistry 2014;42(9):1326–31. [Google Scholar]
  • 30.Venkateswaran K, Raghuveeran C, Gopalan N, Agarwal G, Kaushik M, Vijayaraghavan R. Monitoring of haemoglobin-methyl isocyanate adduct by high-performance liquid chromatography with diode array detector. Biochemistry international 1992;28(4):745–50. [PubMed] [Google Scholar]
  • 31.Mráz J, Cimlová J, Stránský V, Nohová H, Kičová R, Šimek P. N-Methylcarbamoyl-lysine adduct in globin: a new metabolic product and potential biomarker of N, N-dimethylformamide in humans. Toxicology letters 2006;162(2–3):211–8. [DOI] [PubMed] [Google Scholar]
  • 32.Kaushik M, Sikder A, Jaiswal D. A convenient laboratory synthesis of methyl isocyanate. Current Science 1987;56(19):1008–9. [Google Scholar]
  • 33.Shah VP, Midha KK, Findlay JW, Hill HM, Hulse JD, McGilveray IJ, et al. Bioanalytical method validation—a revisit with a decade of progress. Pharmaceutical research 2000;17(12):1551–7. [DOI] [PubMed] [Google Scholar]
  • 34.Taverniers I, De Loose M, Van Bockstaele E. Trends in quality in the analytical laboratory. II. Analytical method validation and quality assurance. TrAC Trends in Analytical Chemistry 2004;23(8):535–52. [Google Scholar]
  • 35.Food and Drug Administration. Guidance for Industry: Bioanalytical Method Validation. In: Center for Drug Evaluation and Research (CDER), Center for Veterinary Medicine (CVM), editors.: U.S. Department of Health and Human Services; 2001. [Google Scholar]
  • 36.Gant J, Dolan J, Snyder L. Systematic approach to optimizing resolution in reversed-phase liquid chromatography, with emphasis on the role of temperature. Journal of Chromatography A 1979;185:153–77. [Google Scholar]
  • 37.Wynckel A, Randoux C, Millart H, Desroches C, Gillery P, Canivet E, et al. Kinetics of carbamylated haemoglobin in acute renal failure. Nephrology Dialysis Transplantation 2000;15(8):1183–8. [DOI] [PubMed] [Google Scholar]
  • 38.Kwan J, Carr E, Bending M, Barron J. Determination of carbamylated hemoglobin by high-performance liquid chromatography. Clinical chemistry 1990;36(4):607–10. [PubMed] [Google Scholar]
  • 39.O’Donnell S, Mandaro R, Schuster TM, Arnone A. X-ray diffraction and solution studies of specifically carbamylated human hemoglobin A. Evidence for the location of a proton-and oxygen-linked chloride binding site at valine 1 alpha. Journal of Biological Chemistry 1979;254(23):12204–8. [PubMed] [Google Scholar]
  • 40.Manandhar E, Maslamani N, Petrikovics I, Rockwood GA, Logue BA. Determination of dimethyl trisulfide in rabbit blood using stir bar sorptive extraction gas chromatography-mass spectrometry. Journal of Chromatography A 2016;1461:10–7. [DOI] [PubMed] [Google Scholar]
  • 41.Bhandari RK, Manandhar E, Oda RP, Rockwood GA, Logue BA. Simultaneous high-performance liquid chromatography-tandem mass spectrometry (HPLC-MS-MS) analysis of cyanide and thiocyanate from swine plasma. Analytical and bioanalytical chemistry 2014;406(3):727–34. [DOI] [PubMed] [Google Scholar]
  • 42.Stutelberg MW, Vinnakota CV, Mitchell BL, Monteil AR, Patterson SE, Logue BA. Determination of 3-mercaptopyruvate in rabbit plasma by high performance liquid chromatography tandem mass spectrometry. Journal of Chromatography B 2014;949:94–8. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 43.Krouwer J, Rabinowitz R. How to improve estimates of imprecision. Clinical Chemistry 1984;30(2):290–2. [PubMed] [Google Scholar]
  • 44.Görgényi M, Dewulf J, Van Langenhove H, Héberger K. Aqueous salting-out effect of inorganic cations and anions on non-electrolytes. Chemosphere 2006;65(5):802–10. [DOI] [PubMed] [Google Scholar]
  • 45.Hey MJ, Jackson DP, Yan H. The salting-out effect and phase separation in aqueous solutions of electrolytes and poly (ethylene glycol). Polymer 2005;46(8):2567–72. [Google Scholar]

RESOURCES