Urinary bromophenols phase II conjugates: A novel human exposure biomarker for PBDEs Ka-Lok Ho1, Bonnie Mei-Wah Fong2,3, Yi Wan4, Sidney Tam3, John P. Giesy1,4,5, Kelvin Sze-Yin Leung2, Michael Hon-Wah Lam1* Key Laboratory for Marine Pollution, Department of Biology & Chemistry, City University of Hong Kong, Hong Kong SAR, 2Department of Chemistry, Hong Kong Baptist University, Hong Kong SAR, 3Department of Clinical Biochemistry, Queen Mary Hospital, Hong Kong SAR, 4Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan S7N 5B3, Canada, 5Department of Zoology and Center for Integrative Toxicology, Michigan State University, East Lansing, MI, USA 1. Introduction Human adipose tissues and blood are the most frequently analyzed samples for the estimation of population exposure to POPs e.g. PBDEs. However, sampling of these tissues are intrusive operations and it is usually difficult to carry out large-scale survey. Sampling of human breast milk can be considered a non-intrusive process, but samples are only restricted to lactating women of a narrow range of ages. It may not be able to truly reflect the level of contaminant exposure to the population. Thus, We aim to develop non-intrusive, representative and convenient exposure markers for selected environmental contaminants. Sampling of human urine is a truly non-intrusive process and samples are much easier to obtain from voluntary donors, for large-scale exposure surveys. It would be ideal if the presence of PBDE metabolites / PBDE congeners in human urine can be used as biomarkers for human exposure to PBDEs. Pharmacokinetic and toxicokinetic studies of BDE-47 and BDE-99 in mammalian models have already identified the presence of Phase II metabolites, mainly dibromophenols (DBPs), tribromophenol (TBPs) glucuronide and sulfate conjugates, in urine samples. Table 2a Table 2b Human plasma samples (n = 100) Min – Max % of Detection 0.01 – 23.47 100 (ng / g l.w. ) 6.38 ± 4.72 ΣBDEs Human urine samples (n = 100) Mean ± S.D. Mean ± S.D. ΣMeO-BDEs 0.94 ± 1.39 N.D. – 6.87 89 ΣOH-BDEs 2.69 ± 2.16 N.D. – 8.88 82 ΣBRPs 1.90 ± 1.84 N.D. – 7.18 84 % of Min – Max (µg / g creatinine) Detection 2,4-DBPG 1.09 ± 3.15 N.D. – 23.81 71 2,4- DBPS 0.21 ± 0.34 N.D. – 2.08 86 2,4,6- TBPG 5.16 ±14.76 N.D. – 102.21 68 2,4,6- TBPS 0.22 ± 0.42 N.D. – 2.93 94 Table 2a. Mean Concentration of ΣPBDE, ΣMeO-BDEs, ΣOH-BDEs & ΣBromophenols in human plasma Table 2b. Mean Concentration of bromophenols glucuronide and sulfate conjugates in human urine 3. Linear Regression & Correlation Σln[BP-glucuronide] and Σln[BP-sulfate] in human urine increases with increasing concentration of ΣPBDEs in the human plasma 20 Y = 5.616 + 1.2939x 18 2 r = 0.2582 16 ΣPBDEs (ng/g lipid Wieght) 1State 14 12 ΣPBDEs & ΣBRPs are statistically significant in accounting for the presence of bromophenols glucuronide and sulfate conjugates in human urine 10 8 6 4 2 Pearson product moment correlation shows a positive, moderate correlation between ΣPBDEs in human plasma and Σ[BPglucuronide] and Σ[BP-sulfate] in human urine while the other determinants show negatively correlated 0 -2 -3 -2 -1 0 1 2 3 4 5 ΣlnBromophenol glucuronide and sulfate conjugates Fig. 3a. Scattered plot of ΣBP conjugates in human urine against ΣPBDEs in human plasma 2. Sample Collection & Analytical Methods Parallel blood plasma and urine samples from 100 adult voluntary donors (50 males, 50 females) have been collected. Extraction method of individual PBDE, OH-BDE, MeO-BDEs, and bromophenols in human plasma was followed the published method with slightly modifications Solid phase extraction (Oasis® WAX) was developed in house and adopted to extract bromophenols glucuronide and sulfate conjugates in human urine. Multiple Linear Regression MeO-BDEs, OH-BDEs, BRPs were identified in human plasma samples with lower concentrations compared to their parent PBDEs. Bromophenol glucuronide and sulfate conjugates were quantified in human urine samples. Moment To further explore the correlation between PBDEs in the blood plasma and bromophenol β P VIF r P metabolites in the urine, multivariant linear ΣPBDEs 3.568 <0.001 1.132 0.508 <0.001 regression models for those Phase II ΣMeO-BDEs 1.283 0.204 1.146 -0.243 0.0211 metabolites with their corresponding parent ΣOH-BDEs 0.284 0.777 1.485 -0.0981 0.378 BDE congeners: i.e. BDEs, MeO-BDEs, OH-BDEs ΣBRPs 2.952 0.004 1.364 -0.329 0.002 and bromophenols with 2,4-dibromo- and Table 3a. Significant predictors of the urinary concentration of bromophenol 2,4,6-tribromo substitution, were examined. conjugates (natural log transformed) Adjusted R2 0.358 With eliminating some influences cases, the goodness of fits (R2) are improved a lot in both models. 3. PBDE Concentrations The population exposure of PBDEs in Hong Kong was found to be comparable to that in other major cities in Asia and Europe, but lower than that in the Northern America and other industrialized regions. Pearson Product lnΣ2,4-dibromophenol conjugates Pearson Product Multiple Linear Regression Adjusted R2 Moment PBDEs are taken a great part into account the presence of bromophenol glucuronide and sulfate conjugate in urine 0.828 β P Model summary for lnΣ2,4,6-tribromophenol conjugates VIF r P Pearson Product Multiple Linear Regression Σ2,4-Dibromo-BDEs 13.599 <0.001 1.128 0.898 Adjusted R2 Σ2,4-Dibromo- 2.316 0.025 1.172 -0.278 Moment <0.001 0.749 β P VIF r P Σ2,4,6-Tribromo-BDEs 12.330 <0.001 1.018 0.863 <0.001 Σ2,4,6-TBP 1.196 0.237 1.018 -0.105 0.346 0.001 MeO-BDEs Σ2,4-Dibromo-OH- 1.907 0.062 1.30 -0.0926 0.414 BDEs Σ2,4-DBP 0.785 0.436 1.173 -0.154 0.195 Table 3c. Significant predictors of the urinary concentration of 2,4,6tribromophenol conjugates (natural log transformed data) Table 3b. Significant predictors of the urinary concentration of 2,4dibromophenol conjugates (natural log transformed data) Y = 1.2939 + 0.1891x 1.8 Σ2,4,6-Tribromo-BDEs (ng/g lipid Wieght) Σ2,4-Dibromo-BDEs (ng/g lipid Wieght) 2.0 2 r = 0.8066 1.6 1.4 1.2 1.0 0.8 0.6 0.4 0.2 -6 -4 -2 0 2 4 Y = 0.147 + 0.025x 0.25 2 r = 0.7455 0.20 0.15 0.10 0.05 0.00 -4 -2 0 2 4 6 Σln2,4,6-Tribromophenol glucuronide and sulfate conjugates Σln2,4-Dibromophenol glucuronide and sulfate conjugates Fig. 3b. Scattered plots of ΣBP-conjugates in human urine vs Σ(structural analog)BDEs n blood plasma: (Left) Σ2,4-dibromophenol conjugates vs Σ2,4-dibromo-BDEs & (Right) Σ2,4,6-tribromophenol conjugates vs Σ2,4,6-tribromo-BDEs 4. Summary To the best of our knowledge, this is the first study to show a significant relationship between plasma PBDEs and urinary bromophenols conjugates in human. This result is important because it confirms that BRP-conjugates in human urine are derived from PBDEs but not bromophenols and the controversial BDE-metabolites, such as OMeBDEs and OH-BDEs. High correlation factors indicate that these urinary bromophenols conjugates are promising biomarkers for the assessment of population PBDE exposure. 5. Acknowledgement: Fig. 2a. International comparisons of BDE congeners in human blood sample This work is supported by a grant from Research Grants Council of the Hong Kong Special Administrative Region, China [Reference No. CityU 9041623]