| Literature DB >> 35655100 |
Fabian Gauch1, Klaus Abraham1, Bernhard H Monien2.
Abstract
Various genotoxic carcinogens ubiquitously present in the human environment or respective reactive metabolites form adducts in DNA and proteins, which can be used as biomarkers of internal exposure. For example, the mass spectrometric determination of Val adducts at the N-termini of hemoglobin (Hb) peptide chains after cleavage by an Edman degradation has a long tradition in occupational medicine. We developed a novel isotope-dilution UHPLC-MS/MS method for the simultaneous quantification of Val adducts of eight genotoxic substances in Hb after cleavage with fluorescein-5-isothiocyanate (FIRE procedure™). The following adducts were included [sources in square brackets]: N-(2,3-dihydroxypropyl)-Val [glycidol], N-(2-carbamoylethyl)-Val [acrylamide], N-(2-carbamoyl-2-hydroxyethyl)-Val [glycidamide], N-((furan-2-yl)methyl)-Val [furfuryl alcohol], N-(trans-isoestragole-3'-yl)-Val [estragole/anethole], N-(3-ketopentyl)-Val [1-penten-3-one], N-(3-ketooctanyl)-Val [1-octene-3-one], and N-benzyl-Val [benzyl chloride], each of which was quantified with a specific isotope-labeled standard. The limits of quantification were between 0.014 and 3.6 pmol/g Hb (using 35 mg Hb per analysis); other validation parameters were satisfactory according to guidelines of the U.S. Food and Drug Administration. The quantification in erythrocyte samples of human adults (proof of principle) showed that the median levels of Hb adducts of acrylamide, glycidamide, and glycidol were found to be significantly lower in six non-smokers (25.9, 12.2, and 4.7 pmol/g Hb, respectively) compared to those of six smokers (69.0, 44.2, and 8.6 pmol/g Hb, respectively). In summary, the method surpasses former techniques of Hb adduct quantification due to its simplicity, sensitivity, and accuracy. It can be extended continuously with other Hb adducts and will be used in epidemiological studies on internal exposure to carcinogens.Entities:
Keywords: Biomarker; Edman degradation; Hemoglobin adduct; Internal exposure
Mesh:
Substances:
Year: 2022 PMID: 35655100 PMCID: PMC9293867 DOI: 10.1007/s00216-022-04143-y
Source DB: PubMed Journal: Anal Bioanal Chem ISSN: 1618-2642 Impact factor: 4.478
Fig. 1Chemical structures of the FTH analytes released after FITC–mediated cleavage of modified Val residues from the N-termini of hemoglobin
Validation parameters for the analyses of FTH conjugates of modified Val residues cleaved by FITC from the N-termini of Hb
| AA- | 65.4 ± 13.0 | 0.25–250 | 0.5 | 0.71 | 87.1 |
| GA- | 67.4 ± 6.3 | 0.25–250 | 0.5 | 0.71 | 53.2 |
| DHP- | 68.9 ± 7.7 | 0.25–250 | 0.5 | 0.71 | 44.5 |
| FFA- | 53.9 ± 4.5 | 1–100 | 2.5 | 3.6 | 32.9 |
| [13C5,15 N]IES-Val-FTH | 66.0 ± 8.5 | 0.005–10 | 0.01 | 0.014 | 1.8 |
| [13C5,15 N]Bn-Val-FTH | 60.7 ± 3.6 | 0.01–10 | 0.025 | 0.036 | 22.1 |
| [13C5,15 N]Ko-Val-FTH | 67.0 ± 6.0 | 0.01–10 | 0.025 | 0.036 | − 1.0 |
| [13C5,15 N]Kp-Val-FTH | 67.8 ± 6.6 | 0.025–100 | 0.05 | 0.071 | 36.5 |
Due to the background of the adducts in human erythrocyte samples, the validation parameters were determined using the respective isotope-labeled compounds
aRecovery of the sample preparation; mean values and SD of six samples
bThe lower limit of the linear range marks the limit of detection (LOD)
cThe LOQ (pmol/g Hb) was calculated with the standard parameters of 35 mg Hb used for the Edman degradation and a final sample volume of 50 μL
Fig. 2UHPLC-MS/MS chromatograms of the quantifier traces (blue lines) from an Edman degradation sample containing AA-Val-FTH (a, m/z 560.2 → 445.0), GA-Val-FTH (b, m/z 576.2 → 531.0), DHP-Val-FTH (c, m/z 563.3 → 503.2), FFA-Val-FTH (d, m/z 569.1 → 390.0), IES-Val-FTH (e, m/z 635.1 → 445.0), Bn-Val-FTH (f, m/z 579.3 → 449.9), Ko-Val-FTH (g, m/z 615.3 → 529.1), and Kp-Val-FTH (h, m/z 573.3 → 489.1), which were normalized to 100% signal intensity. The transitions of the respective isotope-labeled standard compounds (black lines) were adjusted to 50% signal intensity. Absolute intensities of analyte peaks and standard compounds are given. The peak areas correspond to nominal concentrations of 10 nmol/L for all isotope-labeled standard compounds, i.e., 0.1 pmol injected on-column. The chromatographic differentiation of GA-Val-FTH (panel b) and DHP-Val-FTH (panel c) into two peaks reflects the formation of two diastereomers from the nucleophilic attack of valine nitrogens at the terminal carbons of the epoxide rings of glycidamide or glycidol, respectively [23]
CV (%) of five (interday precision) or six (intraday precision) independent analyses at three different concentration levels, corresponding to the respective LOQ, 5 × LOQ, and 25 × LOQ
| Analyte | Intraday | Interday | ||||
|---|---|---|---|---|---|---|
| AA- | 17.4 | 8.1 | 7.2 | 12.7 | 3.0 | 4.2 |
| GA- | 9.0 | 10.3 | 9.8 | 11.9 | 13.9 | 8.6 |
| DHP- | 9.1 | 5.3 | 9.0 | 6.4 | 10.2 | 8.7 |
| FFA- | 4.2 | 4.7 | 9.2 | 11.1 | 5.7 | 5.6 |
| [13C5,15 N]IES-Val-FTH | 12.9 | 9.5 | 6.5 | 6.7 | 8.4 | 5.8 |
| [13C5,15 N]Bn-Val-FTH | 10.3 | 7.1 | 7.6 | 10.8 | 5.6 | 5.1 |
| [13C5,15 N]Ko-Val-FTH | 6.5 | 6.8 | 5.4 | 8.9 | 3.4 | 4.1 |
| [13C5,15 N]Kp-Val-FTH | 8.2 | 6.6 | 1.2 | 9.9 | 5.7 | 5.9 |
Due to the presence of background levels in human Hb, the analyses were performed with the isotope-labeled compounds
Fig. 3Levels of different Val adducts in blood samples of 12 adults of the RBVD study (data from 6 non-smokers and 6 smokers are represented by green boxes and gray boxes, respectively). The upper panel shows the adducts of common heat-induced contaminants AA-Val, GA-Val, DHP-Val, and FFA-Val, and the lower panel shows the adducts of IES-Val, Bn-Val, Ko-Val, and Kp-Val. Lines and boxes represent median values and the lower and upper quartiles, respectively, and the error bars represent the 10th and 90th percentiles. The levels of AA-Val, GA-Val, and DHP-Val from non-smokers and smokers were significantly different (* p < 0.05, ** p < 0.005, Mann–Whitney rank-sum test)
Median levels of the adducts (pmol/g Hb) as well as minimum and maximum values in brackets in erythrocyte samples of human study participants of the current study in comparison to data from previous studies
| Adducta | Source | Adduct level, | Adduct levels, | Ref | ||||
|---|---|---|---|---|---|---|---|---|
| AA-Val | Acrylamide | 25.9 (16.4–41.9) | 69.0 (22.0–770) | 39.6 (14.7–92.4) | 30 | 137 (32.1–371) | 30 | [ |
| GA-Val | Glycidamide | 12.2 (9.6–18.5) | 44.2 (12.0–378) | 34.1 (11.2–96.6) | 30 | 96.1 (25.4–247) | 30 | [ |
| DHP-Val | Glycidol | 4.7 (2.2–4.7) | 8.6 (5.8–23.5) | 6.2 (1.4–16) | 42 | [ | ||
| 4.0 (3.2–5.1) | 11 | [ | ||||||
| 10.3 (6.3–14.0) | 6 | 23.4 (18.1–31.4) | 6 | [ | ||||
| FFA-Val | Furfuryl alcohol | 11.5 (8.9–14.0) | 10.5 (7.5–15.6) | 14.1 (8.2–26.3) | 59 | 17 (11.2–21.4) | 13 | [ |
| IES-Val | Estragole | 0.032 (0.02–0.058) | 0.017 (< LOQ–0.034) | 0.016 (0.012–0.047) | 14 | – | [ | |
| Bn-Val | Benzyl chloride | 0.22 (0.06–0.37) | 0.09 (0.05–0.14) | – | – | |||
| Ko-Val | 1-Octen-3-one | 2.52 (2.17–2.84) | 2.48 (1.7–3.01) | 62 ± 15 (44–91)d | 12 | [ | ||
| Kp-Val | 1-Penten-3-one | 4.21 (3.49–4.62) | 4.15 (3.59–5.11) | 43 ± 14 (26–68)e | 6 | 38 ± 10 (25–53)e | 6 | [ |
aThe adducts may not be formed exclusively from the depicted precursors, e.g., IES-Val is formed from estragole and trans-anethole, and Bn-Val, although discussed primarily in relation to benzyl chloride exposure, may also be formed from benzyl bromide or benzaldehyde
bFrom the multitude of data on AA-Val and GA-Val, we selected an exemplary study with German participants
cThe data was reported in pmol/g globin
dAdduct levels were estimated using a calibration curve with peak area ratios of AA-Val-FTH/AA-d7-Val-FTH. There was no significant difference between the adduct levels in blood samples from non-smoker and smokers (each n = 6)
eValues were reported as mean ± SD