[Determination of organophosphate diesters in facility vegetable soils using ultra-high performance liquid chromatography-electrostatic field orbitrap high resolution mass spectrometry].

Abstract

Organophosphate diesters (Di-OPEs) are biotic or abiotic degradation products of organophosphate esters (OPEs). Current analytical methods focus on detecting Di-OPEs in human urine. Human exposure to Di-OPEs in environmental matrices has not been systematically studied. Soil plays an important role in the environmental migration and transformation of organic pollutants. Previous studies found that OPEs are ubiquitous in soil. However, few studies reported OPEs metabolite pollution in soil, especially in facility vegetable soil. In this study, an ultra-high performance liquid chromatography-electrostatic field orbitrap high resolution mass spectrometry (UPHLC-Orbitrap HRMS) method was developed for the determination of five Di-OPEs (bis(2-chloroethyl) phosphate (BCEP), bis(1,3-dichloro-2-propyl) phosphate (BDCP), di-n-butyl phosphate (DnBP), diphenyl phosphate (DPhP), and bis(2-ethylhexyl) phosphate (DEHP)) in the facility vegetable soil. The pretreatment process and chromatographic and mass spectrometric conditions were optimized in the present study. Comparative study of the purification effects of different solid-phase extraction columns showed that Oasis WAX cartridge had best purification efficiency for the five Di-OPEs. The cartridge was first activated using 3 mL methanol, 3 mL methanol containing 5% (v/v) ammonia, and 3 mL 0.1 mol/L sodium acetate-acetic acid buffer solution. Then, the cartridge was rinsed with 3 mL of 30% (v/v) methanol aqueous solution, and finally eluted using 8 mL methanol containing 5% (v/v) ammonia. The effects of mobile phase (with respect to solvent composition and flow rate) and column temperature on the shape and intensity of chromatographic peaks were studied. The optimized UHPLC conditions were as follows: chromatographic column, Thermo Accucore RP-MS; column temperature, 30 ℃; mobile phase, 0.2 mmol/L ammonium acetate aqueous solution and methanol; flow rate, 0.2 mL/min. In the UHPLC-Orbitrap HRMS experiment, the five Di-OPEs were analyzed in full MS mode with negative ionization. Instrumental parameters, such as sheath gas and auxiliary gas, were optimized to determine the MS conditions. The optimized Orbitrap HRMS conditions were as follows: heating electrospray ionization source (HESI), full MS mode with negative ionization; scan range, m/z 100-500; ion transfer tube temperature, 320 ℃; automatic gain control of target particle count, 1×10⁶; sheath gas flow rate, 8.58 L/min; auxiliary gas flow rate, 17.40 L/min; spray voltage, 3.2 kV; and S-lens voltage, 50 V. The limits of detection and quantification were 0.001-0.047 ng/g and 0.004-0.156 ng/g, respectively. The correlation coefficients of the calibration curve were 0.9985-0.9999. At three spiked levels, 5.0, 25.0, and 50.0 ng/g, the recoveries of the five Di-OPEs ranged from 56.9% to 133.0% with relative standard deviations of 4.4%-18.9%. The established method was applied to the analysis of the five Di-OPEs in 16 facility vegetable soils. The detection frequencies of the five Di-OPEs exceeded 60% in all soil samples, indicating that the Di-OPEs were ubiquitous in the facility vegetable soil. The contents of the five Di-OPEs in the facility vegetable soil samples ranged from 2.53-6.94 ng/g. DnBP (1.37-3.20 ng/g) and DPhP (0.47-2.44 ng/g) were the predominant congeners in the facility vegetable soil samples, accounting for 23.4%-68.8% and 16.3%-35.9% of the five Di-OPEs, respectively. The developed method is simple, sensitive, and reproducible and can be used effectively for the determination of Di-OPEs in soil. The results of this study will be helpful for understanding the environmental behavior of Di-OPEs and their human exposure in facility vegetable soils.