Abstract

Human beings are inevitably exposed to ubiquitous phthalate esters (PAEs). Processed, packaged foods are popular nowadays, in which emulsifiers are frequently added as food additives. It is unclear how emulsifiers affect the bioavailability of ingested PAEs contaminants and their toxicities. The purposes of our study were to explore whether food emulsifier Glycerin Monostearate (GMS) could increase the internal exposure levels of six priority controlled PAEs and affect their reproductive toxicities when male rats are exposed to PAEs mixture (MIXPs). The male rats were exposed to MIXPs by gavage for thirty days in combination with or without given GMS. Phthalate monoesters (MPAEs), primary metabolites of PAEs, in rat urine were used as biomarkers to predict the internal exposure levels of the six PAEs, and their concentrations were determined using UPLC-MS. The reproductive toxicity was evaluated using serum testosterone levels test and histopathology of testes. Results showed that compared to PAEs exposure alone, the internal exposure levels of PAEs increased by 30%-49% in the presence of GMS. PAEs exposure led to the reduction of testosterone level by 23.4%-42.1% in the presence and absence of GMS, respectively, compared to the baseline. Testosterone levels in MIXPs+GMS and DEHP+GMS group were decreased by 9.1% and 13.6%, respectively, compared with MIXPs and DEHP group. Histopathology showed that injuries of testis (deciduous spermatids) were observed, and GMS exacerbated the injuries. The results indicated food emulsifiers chronically taken up might increase safety risks of food PAEs contaminants.

Highlights

  • Phthalate esters (PAEs) are commonly used as plasticizer to increase the flexibility, pliability and elasticity of polyvinyl chloride (PVC) plastics, and widely used in cosmetics, personal care products, food packaging, children’s toys and medical products [1,2,3,4]

  • In human and animal body, PAEs are rapidly metabolized to their corresponding monoesters, and some of which can be further metabolized to the oxidation products of their lipophilic aliphatic side chain

  • dimethyl phthalate (DMP) is metabolized to MMP, while di(2-ethyhexyl) phthalate (DEHP) is metabolized to MEHP, which can be further metabolized to MEHHP, MEOHP and so on [5]

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Summary

Introduction

Phthalate esters (PAEs) are commonly used as plasticizer to increase the flexibility, pliability and elasticity of polyvinyl chloride (PVC) plastics, and widely used in cosmetics, personal care products, food packaging, children’s toys and medical products [1,2,3,4]. Some PVC plastic products contain on average 30~45% PAEs by weight [4, 5]. Since PAEs are not chemically bound to the PVC, they can quite be released into environment from PVC products [6, 7]. PAEs can migrate into foods from plastic containers and/or environment, thereby indirectly entering human body. The total PAEs concentrations in fish from HongKong market ranged from 1.57 to 7.10 μg/g [11], and di(2-ethyhexyl) phthalate (DEHP) level was about 3 μg/g in pork from New York market [12]. Di(n-butyl) phthalate (DBP) and DEHP levels in cow milk packed in polyethlene containers reached 75 ng/mL and 195 ng/mL, respectively [13], and DEHP was about 3.6–101 ng/mL in light alcoholic drinks and soft drinks [14]

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