Does External Exposure of Glycidol-Related Chemicals

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Does External Exposure of Glycidol-Related Chemicals toxics Communication Does External Exposure of Glycidol-Related Chemicals Influence the Forming of the Hemoglobin Adduct, N-(2,3-dihydroxypropyl)valine, as a Biomarker of Internal Exposure to Glycidol? Yuko Shimamura 1, Ryo Inagaki 1, Hiroshi Honda 2 and Shuichi Masuda 1,* 1 School of Food and Nutritional Sciences, University of Shizuoka, 52-1 Yada, Suruga-ku, Shizuoka 422-8526, Japan; [email protected] (Y.S.); [email protected] (R.I.) 2 KAO Corporation, R&D Safety Science Research, 2606 Akabane, Ichikai-Machi, Haga-Gun, Tochigi 321-3497, Japan; [email protected] * Correspondence: [email protected]; Tel.: +81-54-264-5528 Received: 2 November 2020; Accepted: 11 December 2020; Published: 13 December 2020 Abstract: Glycidyl fatty acid esters (GE) are constituents of edible oils and fats, and are converted into glycidol, a genotoxic substance, in vivo. N-(2,3-dihydroxypropyl)valine (diHOPrVal), a hemoglobin adduct of glycidol, is used as a biomarker of glycidol and GE exposure. However, high background levels of diHOPrVal are not explained by daily dietary exposure to glycidol and GE. In the present study, several glycidol-related chemicals (glycidol, ( )-3-chloro-1,2-propanediol, glycidyl oleate, ± epichlorohydrin, propylene oxide, 1-bromopropane, allyl alcohol, fructose, and glyceraldehyde) that might be precursors of diHOPrVal, were administered to mice, and diHOPrVal formation from each substance was examined with LC-MS/MS. DiHOPrVal was detected in animals treated with glycidol and glycidyl oleate but not in mice treated with other chemicals (3-MCPD, epichlorohydrin, propylene oxide, 1-bromopropane, allyl alcohol, fructose, and glyceraldehyde). The amount of diHOPrVal per administered dose produced from other chemicals was negligible compared to the amounts associated with dietary glycidol and GE. The present study provides important knowledge for exploring other sources for internal exposure to glycidol. Keywords: glycidol; glycidyl fatty acid esters; Hb adduct; N-(2.3-dihydroxypropyl)valine 1. Introduction Glycidyl fatty acid esters (GE) are process contaminants, formed in a deodorization process under high-temperature conditions during the production of edible oils. Diacylglycerol oil was found to contain GE at considerably higher levels than other commercial edible oils. GEs were also formed in heat treatment of saltwater fish, meat patties, etc., especially at high temperature using a charcoal grill [1,2]. Furthermore, the formation of GE can occur in all refined edible oils and processed foods made using these oils [3,4], infant formula [5], baby foods [6], etc. GE are degraded in vivo by lipase to produce glycidol (2,3-epoxy-1-propanol), a reactive epoxide. Glycidol is a confirmed rodent carcinogen in a National Toxicology Program (NTP) study [7]. The genotoxicity is well characterized in vitro [8,9] and in vivo [10]. Human exposure is a concern because glycidol would be produced from dietary GE. Hemoglobin adducts are used as biomarkers for evaluating long-term exposure to various reactive chemicals. N-(2,3-dihydroxypropyl)valine (diHOPrVal) is a hemoglobin adduct of glycidol and is used as a marker for internal exposure to glycidol [11–14]. A total of eleven healthy participants consumed a daily portion of about 36 g of commercially available palm fat (8.7 mg glycidol/kg) over Toxics 2020, 8, 119; doi:10.3390/toxics8040119 www.mdpi.com/journal/toxics Toxics 2020, 8, x FOR PEER REVIEW 2 of 9 Toxics 2020, 8, 119 2 of 9 consumed a daily portion of about 36 g of commercially available palm fat (8.7 mg glycidol/kg) over 4 weeks. The mean daily glycidol exposure, as estimated from the adduct levels of the participants 4before weeks. the The intervention mean daily period glycidol (background exposure, levels as estimated of diHOPrVal), from the was adduct 0.94 levels µg/kg of body the participantsweight [15]. beforeAdditionally, the intervention diHOPrVal period levels (background were used levelsto estimate of diHOPrVal), a continuous was exposure 0.94 µg/kg of body1.4 μg/kg/day weight [15 of]. Additionally,glycidol in 50 diHOPrValchildren aged levels approximately were used to12 estimate years old a [16]. continuous These values exposure are ofsignificantly 1.4 µg/kg/ dayhigher of glycidolthan the in European 50 children Food aged Safety approximately Authority 12estimates years old of [ 16intake]. These for valuesadults areand significantly children. One higher possible than thereason European for this Food discrepancy Safety Authority is exposure estimates to other of chemicals intake for that adults form and diHOPrVal. children. One possible reason for thisTheoretically, discrepancy diHOPrVal is exposure might to other originate chemicals from that other form precu diHOPrVal.rsors (Figure 1). One possibility is the foodTheoretically, contaminant diHOPrVal 3-monochloropropane might originate from-1,2-diol other (3 precursors-MCPD), which (Figure often1). One forms possibility in foods is the in foodparallel contaminant with glycidol 3-monochloropropane-1,2-diol [17]. GE are also formed from (3-MCPD), 3-MCPD which esters often in neutral, forms acidic, in foods and in parallelalkaline withmedia glycidol [18]. Furthermore, [17]. GE are also ally formedl alcohol from can 3-MCPD theoretically esters in be neutral, converted acidic, to and diHOPrVal, alkaline media and [18the]. Furthermore,glyceraldehyde allyl hemoglobin alcohol can adduct theoretically might be be converted converted to to diHOPrVal diHOPrVal, under and reducing the glyceraldehyde conditions hemoglobin[19]. Hondaadduct et al. mightreported be converteda positive to correlation diHOPrVal between under reducing intake conditionsof one food [19 ].item Honda (western et al. reportedconfection a positiveery) and correlation diHOPrVal between levels among intake ofthe one 70 foodfood item items (western and 97 confectionery)nutrients in a andfood diHOPrVal frequency levelsquestionnaire among the[12], 70 although food items Aasa and et al. 97 did nutrients not confirm in a foodthe importance frequency of questionnaire sweets intake [12 [16].], although Fructose Aasain western et al. did confectionery not confirm theis importancemetabolized of to sweets glyceraldehyde intake [16]. Fructose[20]. Occupational in western confectioneryexposure to isepichlorohydrin metabolized to may glyceraldehyde also result in [ 20diHOPrVal]. Occupational [21]. Ishidao exposure et al. to reported epichlorohydrin glycidol in may urine also samples result inof diHOPrValrats that were [21]. exposed Ishidao to et al.1-bromopropane reported glycidol and inassumed urine samples that propylene of rats that oxide were is exposeda possible to 1-bromopropaneintermediate between and assumed 1-bromopropane that propylene and oxideglycidol is a possible[22]. diHOPrVal intermediate levels between in smokers 1-bromopropane are higher andthan glycidol those in [ 22non].- diHOPrValsmokers [23]. levels On inthe smokers other hand, are higher Eckert than et al. those and inAndreoli non-smokers et al. reported [23]. On that the otherlevels hand, of 2,3- Eckertdihydroxypropyl et al. and Andreoli mercapturic et al. acid, reported a urinary that biomarker levels of 2,3-dihydroxypropyl of glycidol, were correlated mercapturic with acid,urinary a urinary creatinine biomarker but not with of glycidol, smoking were status correlated [24,25]. It with is possible urinary that creatinine chemicals but other not with than smoking glycidol statusmight [24affect,25]. Itthe is possibleformation that of chemicals diHOPrVal. other Although than glycidol several might studies affect the discussed formation other of diHOPrVal. possible Althoughprecursors several of glycidol, studies experimental discussed other verification possible has precursors not been of provided. glycidol, experimentalThe aim of this verification study was has to notexamine been provided.whether Theexternal aim of exposure this study to was glycidol to examine-related whether chemicals external (3 exposure-MCPD, toepichlorohydrin, glycidol-related chemicalspropylene (3-MCPD, oxide, 1-bromopropane, epichlorohydrin, allyl propylene alcohol, oxide, fructose, 1-bromopropane, and glyceraldehyde) allyl alcohol, affect fructose,s levels and of glyceraldehyde)diHOPrVal in vivo affects using levels mice of diHOPrVal. In addition,in vivoadductsusing of mice. epichlorohydrin In addition,adducts and glyceraldehyde of epichlorohydrin were andevaluated. glyceraldehyde were evaluated. FigureFigure 1.1. Examples of possible precursors toto NN-(2,3-dihydroxypropyl)valine-(2,3-dihydroxypropyl)valine cf.cf. [[1616,19].,19]. 2. Materials and Methods 2. Materials and Methods 2.1. Chemicals 2.1. Chemicals Fluorescein isothiocyanate (FITC), glycidol, ( )-3-chloro-1,2-propanediol (3-MCPD) (purity 98.0%), ± and glycidylFluorescein oleate isothiocyanate (purity 98.0%) were(FITC), obtained glycidol, from (±) Sigma-Aldrich-3-chloro-1,2-propanediol (St Louis, MO). (3 Epichlorohydrin,-MCPD) (purity propylene98.0%), and oxide, glycidyl 1-bromopropane, oleate (purity allyl 98.0%) alcohol, were D(-)-fructose, obtained andfrom DL-glyceraldehyde Sigma-Aldrich (St were Louis, obtained MO). Epichlorohydrin, propylene oxide, 1-bromopropane, allyl alcohol, D(-)-13fructose, and DL- from FUJIFILM Wako Pure Chemical Industries Ltd. (Osaka, Japan). L-Valine-( C5) (purity 98.0%) glyceraldehyde were obtained from FUJIFILM Wako Pure Chemical Industries13 Ltd. (Osaka, Japan). used for the synthesis of the internal standard N-(2,3-dihydroxypropyl)-( C5)valine,
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