Effects of Perfluorinated Phosphate Derivatives on Gene Expression in the H4IIE Rat Hepatoma Cell Line Paul D. Jones1,2, Jonathan Naile2,*, Steve Wiseman2, and John P. Giesy2,3,4,5 1 School for Environment and Sustainability, University of Saskatchewan, Saskatoon, SK, Canada. 2 Toxicology Centre, University of Saskatchewan, Saskatoon, SK, Canada3 Department of Biomedical Veterinary Sciences and Toxicology Centre, University of Saskatchewan, Saskatoon, SK, Canada, 4 Zoology Department, Center for Integrative Toxicology, Michigan State University, East Lansing, MI, USA, 5 Department of Biology and Chemistry, City University of Hong Kong, Kowloon, Hong Kong, SAR China. * Corresponding Author’s Phone Number: 306‐966‐5062, Email: paul.jones@usask.ca ABSTRACT Perfluorinated chemicals (PFCs) have gained much recent notoriety due to widespread occurrence in the environment and wildlife and their toxicological effects. Recognition of the potential adverse effects of PFCs has lead to development and use of a variety of alternative compounds, some still containing perfluorinated moieties. Notable among these alternative chemicals are the perfluoroalkyl‐phosphates (PAPs). These compounds are either the phosphonic acid analogs of carboxylic acids or are mono‐, di‐ or tri‐phosphate esters, commonly of fluorotelomer alcohols. During environmental and metabolic breakdown PAPs can be expected to yield a variety of perfluorinated moieties including the parent phosphonic acids and compounds such as FTOHs and potentially perflurocoaboxylates after further degradation of those FTOHs. The objectives of the current study were to determine if PAPs caused the same changes in gene expression as PFCs and whether the gene expression effects of some PAPs were the same as the effects caused by the constituent PFC moieties. Rat hepatoma cells were treated with different PAPs and PFCs at concentrations of 1.0‐ 100 uM for 24 and 72 hrs. RNA was isolated, purified and gene expression was quantitatively measured using Real‐Time PCR. Processes investigated included fatty acid synthesis, cellular communication, and thyroid development. Perfluorophosphonic caused differential gene expression profiles relative to analogous perfluorocarboxylates. For example PFDPA at 10 uM caused 69‐fold induction of Apo A4 while the analogous PFDA caused only 6.4 fold induction of the same gene. Effects of phosphate ester compounds were different from comparable perfluoroalcohols which would be expected to be released by metabolic breakdown. We therefore conclude that PAPs may act through mechanisms of action different from other PFCs and so greater research and understanding of the effects of this emerging chemical group is required. INTRODUCTION RESULTS Perfluorinated compounds (PFCs) have been produced and used in large quantities since the 1950s. While some of the predominant compounds are no longer produced the search for alternative perfluorinated chemicals continues. Perfluoroalkyl phosphates (PFAPs), analogues of the sulphonic and carboxylic acid PFCs have recently been identified in the environment (D’eon et al 2009 Environ. Toxicol. Chem. 28:2101‐2107). Currently two classes of PFPAs are of interest; Perfluoroalkyl phosphate esters (PEs) and the phosphonic acids (PAs). PEs have the potential to release perfluoro moieties when hydrolysed. These moieties may be metabolized to carboxylates in organisms (Fig. 1). Phosphonic acids may possess unique toxic potential due to the presence of the C‐P bond. In this study PEs and PAs were compared to other PFCS (Table 1) with respect to their ability to modulate the expression of several genes. Genes were selected based on the known effects of other PFCs and on their ability to act as markers for critical biochemical functions (Table 2). Abbreviation PFBS PFOS PFBA PFOA PFOPA PFDPA PFHxPA POFPP PHFBP PTEHP Table 1 Chemicals Tested for Effects on Gene Expression Type Name Sulphonic Acid Pefluorobutyl sulphonic acid Sulphonic Acid Pefluorooctyl sulphonic acid Carboxylic Acid Perfluorobutyl carboxylic Acid Carboxylic Acid Perfluorooctyl carboxylic Acid Phosphonic Acid Perfluorooctyl phosphonic acid Phosphonic Acid Perfluorodecyl phosphonic acid Phosphonic Acid Perfluorohexyl phosphonic acid Phosphate Ester Tris (octafluoropentyl) phosphate Phosphate Ester Tris (heptafluorobutyl) phosphate Phosphate Ester Tris (trifluoroethyl) phosphate Chain Length C4 C8 C4 C8 C8 C10 C6 C5 C4 C2 Table 2 Genes Investigated (responses normalized to Glyceraldehyde‐3‐phosphate dehydrogenase) Gene Function Na+/K+ ATPASE Maintenance of cellular osmotic balance PAX 8 (Paired box gene 8) Related to thyroid follicular cell development HEX (Homeobox) Related to thyroid cell differentiation Apo‐A4 (Apolipoprotein A‐IV) Related to fatty acid metabolism RESULTS Fig. 3. Chemical Ordination Based on Gene Expression Fig. 2. Chemical Induced Changes in Gene Expression PFDPA PFDPA PFDPA Tri C5 ester 40 Apo‐A4 40 30 20 PFDPA PFDPA Tri C5 ester PTEHPTri C5 ester PFHxPA PFOPA 30 Fold Induction 50 Fold Induction Na/K ATPase APOA4 60 20 PTEHP PFOS Tri C4 ester PFBA 10.0 1.0 0.1 1 0.0 C 0 0 0 entr onc n atio Carboxylates ) (uM PT PH EH PO FB P FP P P PF FO P H PA PF xP D A PF PA O PF A BA PF O S PF BS PT PH EH PO FB P FP P P PF FO P Hx PA PF P D A PF PA O PF A BA PF O S PF BS Ch em ic al Chemical Class Phosphonic acids Phosphate esters Ch em ic al 10.0 1.0 0.1 0.0 1 0 0 ntr nce Co 0 Tri C4 ester Chemical Class PTEHP Tri C4 ester Tri C4 ester Carboxylates PFBA PFOA PFBA PFBA PFBS PFOA PFOA PFOS PFBA PFBA PFBA PFBA PFBAPFBS PFBS Phosphonic acids PFOA PFOS Tri C4 ester PFOA PFBA PFOA Phosphate esters PFOS PFOS PFOA PFOA PFOA PFOA PFOS PFOS PFBS PFBS PFBS PFBS PAX8 Sulphonic acids PFBS PFBS ATPASE HEX M) n (u atio Fig. 4. Chemical Ordination Based on Thyroid Related Genes PFOA 70 Fold Induction 30 20 10 PFOA PFOA PAX 60 Tri C5 ester PTEHP PFOA 50 PFHxPA PTEHP PFHxPA PTEHP ester PFDPA TriTri C5C5 ester PFOPA PTEHP PFOPA PFDPA PFHxPA 10 40 HEX HEX Fold Induction PTEHP PFOS PFBA Tri C4 ester PFOS Sulphonic acids 40 Tri C5 ester Tri C4 ester PFBS PFBS 00 100. PTEHP Tri C5 ester PFOPA PFHxPA PFHxPA PFOPA PFHxPA PFOPA Tri PTEHP C5 ester PTEHP Tri C5 ester Tri C5 ester PFBA PFOA PFOA PFBS 0 PFDPA PFDPA Tri C5 ester Tri C5 ester Tri C4 ester PFOS .0 100 PTEHP PTEHP Tri C4 ester Tri C4 ester Tri C4 ester PFOS PFOS 10 10 PFHxPA PFHxPA PTEHP Tri C5 ester Tri C5 ester PFOPA PFDPA PFDPA PTEHP PFOPA PFHxPA PFHxPA PFHxPA PFOPA PTEHP 30 20 0 .0 100 PT PH EH PO FB P FP P P PF FO P H PA PF xP D A PF PA O PF A BA PF O S PF BS PT PH EH PO FB P FP P P PF FO P H PA PF xP D A PF PA O PF A BA PF O S PF BS Ch em ic al 10.0 0 Ch em ic al 0 1.0 M) n (u 0 atio ntr nce Co 0.1 0.0 1 Carboxylates Phosphonic acids PFDPA ester Tri Tri C4 C4 ester PFOS PFOS PFOS 10 Chemical Class Tri C5 ester Phosphate esters PFOS Tri C4 ester 10.0 0 .0 100 0 0 1.0 M) n (u 0 atio ntr nce Co 0.1 0.0 1 1 PFBS PFBS PFBS Sulphonic acids PFBA PFBA PFBA PFBSPFBA 0.1 1.0 10.0 PAX8 METHODS CONCLUSIONS Rat hepatoma cells (H4IIE cell line) were cultured under standard conditions, 37ᴼC, 5% CO2. 24 hrs after plating exposure chemicals were added, cell were incubated for 72 hrs. After 72 hrs mRNA was extracted from cultured cells and stored in ‘RNAlater’ until analysis. RT‐PCR was performed using standard methods, all expression values were normalized to the expression of glyceraddehyde‐3‐phosphate dehydrogenase as a house keeping gene. • PFAPs of both classes induced greater changes in Apo‐A4 expression than any of the carboxylic and sulphonic acids tested (Fig. 2). Increased expression of Apo‐A4 has been linked with decreases in feeding responses, and is believed to be a vital signal for lipid uptake, transportation and metabolism. • Of the phosphonic acids tested the C10 (PFDPA) was generally the most potent for alterations in gene expression analogous of the greater potency of the C8‐10 PFCs. • POFPP (C5 ester) induced increased the expression of Na+/K+ ATPase even at the lowest dose tested and was clearly the most potent chemical for this endpoint (Fig. 2). This transporter is involved in osmotic homeostasis this response may be indicative of alterations in membrane permeability. • The expression profile of the phosphate esters overlaps or ‘approaches’ that of the carboxylates suggesting that the metabolic generation of carboxylates may be occurring. • This study clearly demonstrates that PFAPs elicit a range of effects on gene expression that are distinct from those elicited by other PFCs (Fig. 3). Therefore, further studies on the potential modes of action of these emerging contaminants is warranted. • Alteration of PAX 8 and HEX expression by PFAPs, particularly the phosphonic acids (PAs) may be indicative of potential impacts on thyroid function and homeostasis (Fig. 4). Cell culture and exposure (24 and 72 hrs) RNA Extraction cDNA Synthesis Q‐PCR Normalize to G3P‐DH Incubate at 37°C for 72 hrs RNA Extraction and Q‐PCR Acknowledgements This research was supported by a Discovery Grant from the National Science and Engineering Research Council (NSERC) (Project # 326415-07) and a grant from Western Economic Diversification Canada (Projects 6578, 6807). We acknowledge an instrumentation grant from the Canada Foundation for Infrastructure. JPG was supported by the Canada Research Chair program and an at large Chair at the Department of Biology and Chemistry and the Research Centre for Coastal Pollution and Conservation, City University of Hong Kong.