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14 March 2020

A Halogen Bonding Perspective on Iodothyronine Deiodinase Activity

and
Department of Chemistry and Biochemistry, Old Dominion University, Norfolk, VA 23529, USA
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Author to whom correspondence should be addressed.
This article belongs to the Special Issue Halogen Bonding: Insights from Computational Tools

Abstract

Iodothyronine deiodinases (Dios) are involved in the regioselective removal of iodine from thyroid hormones (THs). Deiodination is essential to maintain TH homeostasis, and disruption can have detrimental effects. Halogen bonding (XB) to the selenium of the selenocysteine (Sec) residue in the Dio active site has been proposed to contribute to the mechanism for iodine removal. Polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs) are known disruptors of various pathways of the endocrine system. Experimental evidence shows PBDEs and their hydroxylated metabolites (OH-BDEs) can inhibit Dio, while data regarding PCB inhibition are limited. These xenobiotics could inhibit Dio activity by competitively binding to the active site Sec through XB to prevent deiodination. XB interactions calculated using density functional theory (DFT) of THs, PBDEs, and PCBs to a methyl selenolate (MeSe) arrange XB strengths in the order THs > PBDEs > PCBs in agreement with known XB trends. THs have the lowest energy C–X*-type unoccupied orbitals and overlap with the Se lp donor leads to high donor-acceptor energies and the greatest activation of the C–X bond. The higher energy C–Br* and C–Cl* orbitals similarly result in weaker donor-acceptor complexes and less activation of the C–X bond. Comparison of the I···Se interactions for the TH group suggest that a threshold XB strength may be required for dehalogenation. Only highly brominated PBDEs have binding energies in the same range as THs, suggesting that these compounds may inhibit Dio and undergo debromination. While these small models provide insight on the I···Se XB interaction itself, interactions with other active site residues are governed by regioselective preferences observed in Dios.

1. Introduction

Thyroid hormones (THs) are essential biomolecules involved in many biochemical processes, particularly in early developmental stages [1,2,3,4,5]. The prohormone thyroxine (3,3′,5,5′-tetraiodothyronine, T4), and to a lesser extent, 3,3′,5-triiodothyronine (T3) are secreted from the thyroid gland upon stimulation by thyroid stimulating hormone (TSH) [6]. Transport proteins (TPs), such as thyroglobulin (TBG) and transthyretin (TTR), transport THs to target cells based on metabolic and/or developmental needs [1].
Upon reaching target cells, deiodination by the iodothyronine deiodinase (Dio) family of selenoproteins modulates TH signaling by controlling levels of the active metabolite T3 (Figure 1) [1]. Deiodination of the outer (phenolic) ring or inner (tyrosyl) ring of THs are activating and inactivating pathways respectively. For example, outer-ring deiodination (ORD) of T4 by Type I (Dio1) or Type II (Dio2) deiodinases produces active T3, while inner-ring deiodination (IRD) of T4 by Type III (Dio3, and Dio1 to a lesser extent) produces the inactive metabolite 3,3′,5′-triiodothyronine or reverse T3 (rT3) (Figure 1). Dio3 also lowers T3 concentrations through conversion to 3,3′-diiodothyronine (T2). Deiodination is facilitated by a rare selenocysteine (Sec) residue within the cleft of the active site [7].
Figure 1. Mechanistic pathways of deiodination by each deiodinase with thyroid hormone (TH) substrates. Dio is regioselective for outer-ring or inner-ring deiodination (ORD and IRD, respectively).
Disruption of TH homeostasis by xenobiotics can have long-term negative health effects such as structural abnormalities, cardiovascular diseases, and hypo/hyperthyroidism [1,8]. Organohalogen compounds, such as polybrominated diphenyl ethers (PBDEs) and polychlorinated biphenyls (PCBs), are known endocrine-disrupting compounds that induce a range of developmental and neurodegenerative effects [9,10,11,12,13,14,15,16,17,18,19,20]. Recently, studies have shown that inhibition of Dio activity may be one pathway for disruption [21,22,23,24]. Related halogenated compounds such as polybrominated biphenyls (PBBs) and polychlorinated diphenyl ethers (PCDEs) have been shown to alter TH levels but have not yet been shown to inhibit Dio [25,26,27].
PBDEs are used in commercial products to increase flame resistance (Figure 2a) [28,29]. However, PBDEs contaminate house dust, leading to exposure via ingestion or inhalation [21]. As a result, some formulations, namely the penta- and octa-BDEs, were banned in the early 2000s [30,31]. Industrial runoff of these compounds into the environment has led to bioaccumulation in organisms over time, leading to contamination in wildlife [32,33,34,35,36]. Enzymatic debromination of higher-order PBDEs (>5 Br) contributes to more efficient bioaccumulation [30,37]. Hydroxylated metabolites (OH-BDEs) have been shown to inhibit TRβ in silico and in vitro [38,39]. There is evidence for Dio inhibition by PBDEs and OH-BDEs in fish, birds, and humans [21,37,40,41].
Figure 2. Examples of (a) polybrominated diphenyl ethers (PBDEs)—BDE-47 and 3-HO-BDE-47; (b) polychlorinated biphenyls (PCBs)—PCB-77 and triclosan.
PCBs, like PBDEs, are industrial flame retardants with high chemical stability (Figure 2b) [42,43]. Production of some PCB formulations were banned in the 1970s, but they still contaminate urban areas [44,45,46,47]. These organohalogens are classified into two subcategories—coplanar or dioxin-like (having no ortho chlorines) and non-coplanar or non-dioxin-like (having one or more ortho chlorines). Dioxin-like PCBs are highly toxic, which is often attributed to an assumed structural similarity with tetrachlorodibenzodioxin (TCDD), a known inhibitor of the aryl hydrocarbon receptor (AhR) [48]. Non-dioxin-like PCBs are toxic at higher concentrations and inhibit TBG and TTR [49,50,51,52]. PCBs have been reported to disrupt TH homeostasis through other mechanisms, such as the sodium-iodide symporter (NIS) [51,53,54,55,56]. Limited experimental data suggest that PCBs disrupt TH levels, which could indicate Dio inhibition [57,58,59]. The hydroxylated compound triclosan has been shown to weakly inhibit Dio (Figure 2b) [60].
Halogen bonding (XB) has gained importance in drug design and crystal engineering [61,62,63,64,65,66,67,68,69,70]. Our group has proposed that XB participates in the Dio mechanism through the formation of an initial Se···I interaction between the selenium of the active site Sec residue and a TH iodine (Figure 3) [71]. This mechanism is supported by the work of Mugesh et al. on naphthyl-based deiodinase mimics which display high activity through a combination of halogen and chalcogen bonding [72]. In addition, Schweizer et al. identified potential proton channels in their X-ray structure of the Dio3 catalytic domain that support the XB-based mechanism [7]. Dios prefer the rare Sec residue due to its high nucleophilicity relative to Cys, which is enhanced by deprotonation at physiological conditions. Recent studies by our group explored the possibility that organohalogens like PCBs and PBDEs could inhibit Dio activity by blocking the active site through an X···Se halogen bonding (XB) interaction [28,73].
Figure 3. Proposed halogen bonding-based mechanism for deiodination by Dio adapted from reference [71]. The identities of B and their protonation states have not been determined.
An ongoing debate on the driving forces for the XB interaction has raged in the literature [42,66,74,75,76,77,78,79,80,81,82]. Briefly stated, one side describes XB as driven primarily by electrostatics, where the donor interacts with an area of positive electrostatic potential on the distal end of the R–X bond, commonly called the “σ-hole” [68,83,84]. This “polar flattening” results from electron density depletion along the R–X bond axis, leading to the halogen to adopt an anisotropic, oblate shape [67,85,86,87]. Groups on the other side note charge transfer as a significant contributor to XB and use descriptions in terms of valence bond theory or molecular orbital (MO) interactions related to early contributions by Mulliken [71,80,88,89,90,91,92,93,94]. Our group’s discussion of XB in Dio activity has focused on this latter MO description to define XB as a donor-acceptor interaction between the lone pair of a nucleophile (σlp) and the antibonding orbital (σR-X*) on the acceptor fragment (Figure 4). According to this model, XB is strengthened for (a) Lewis acids with weaker R–X bonds, which have lower lying σR-X* MOs, and (b) stronger Lewis bases due to destabilization of the lp donor MOs. In Dio, a partial explanation for the preference of Sec of Cys is the greater Lewis basicity of the selenolate over the thiolate [71]. In peri-chalcogen-substituted naphthyl-based Dio mimics, strong nucleophiles have higher Dio-like activity (i.e., Se,Se > Se,S > S,S), consistent with the preference for selenium over sulfur [95,96]. Natural Bond Orbital (NBO) theory can be used to calculate the donor-acceptor energy (ΔED→A) as the extent to which donation into the σR-X* acceptor stabilizes of the lp donor MO (Figure 4) [71,97]. The trend in ΔED→A for organohalogens is consistent with increasing XB strength with halogen size. The increased donation into σR-X* leads to more activated C–X bonds (i.e., C–I > C–Br > C–Cl for both Δd(C–X) and ΔED→A) (Figure 4) [28].
Figure 4. XB as described by the molecular orbital (MO) model showing the interaction between a lone pair of a donor and the R–X antibonding orbital, alongside the corresponding average stabilization of the Se donor lone pair by THs, PBDEs, and PCBs as determined by Natural Bond Orbital (NBO) ΔED→A analysis. Units are kcal mol−1. Adapted from reference [66].
Overlap with the donor MO is enhanced when the acceptor σR-X* MO has a greater contribution from the halide AOs. Decreasing the electronegativity from F to I causes the X AOs to destabilize relative to the R fragment, resulting in orbitals with more ‘R’-like character in σR-X while increasing the X contribution (%X) to σR-X* [66]. The shift in the R character of σR-X depletes the electron density along the bond axis only, consistent with the observation of a σ-hole in the electrostatic potential [84]. XB interactions have also been described using a more complex MO diagram for the mixing of both σR-X and σR-X* with the donor MO, resulting in an interaction similar to the 3c4e hypervalent bond observed in the trihalide I3 (Figure 4) [89,90,98,99,100]. Maximization of the overlap between σlp and σR-X* requires a near 180° R–X···Y angle, where Y is the donor. Many protein-ligand XB interactions fall in the range of 140° to 160° [65,101,102,103].

3. Discussion

Modeling the XB interactions of halogenated endocrine disruptors with the Dio active site model SeMe model provide insight into potential mechanisms of inhibition. Xenobiotics such as PBDEs and PCBs may inhibit Dio by forming an X···Se XB interaction to the catalytic Sec in the active site. XB favorability in the order of THs > PBDEs > PCBs agrees with the expected trends (I > Br > Cl). THs generally undergo deiodination by Dios, an exception being 3-T1 which has the weakest I···Se XB interaction of the series. This observation suggests that XB interaction strength with the active site Sec must exceed an energy threshold for deiodination. While some of the highly substituted PBDEs/OH-BDEs have similar interaction energies to THs and may undergo debromination, PCBs have less favorable interactions, suggesting dechlorination by Dio would not be observed.
XB interaction strengths vary by position. The preference for XB at the meta and ortho positions of diphenyl ethers suggests that the substitution pattern of THs may have been selected to facilitate enzymatic deiodination. The position dependence of XB interactions of PBDEs (ortho and meta) and PCBs (meta and para) suggest that these compounds may target Dio types with substitution patterns similar to their preferred substrate [116]. For example, Dio1 performs both ORD (meta-) and IRD (ortho-) (although there is a preference for ORD) with rT3 as its preferred substrate, while Dio2 and Dio3 prefer ORD (meta-) and IRD (ortho-) with T4 and T3, respectively. A PCB, PBDE or related compound with a structure containing solely meta halogens (such as PCB-80 or BDE-80), or its strongest XB interactions at the meta position, may preferentially inhibit Dio2. Likewise, a PCB, PBDE or related compound containing solely ortho chlorines (such as PCB-54 or BDE-54), or its strongest XB interactions at the ortho position, may target Dio3 for inhibition. These preferences will be subject to other interactions within the Dio active site. Understanding the regioselectivity of these preferences may aid in the drug design to target specific Dios.
The conformational preferences of THs and halogenated aromatics will also affect Dio binding. For instance, since PBDEs have the same diphenyl ether core as THs, they may bind to Dio in a similar fashion. Xenobiotics with large halogens, such as THs and PBDEs, may be less able to adapt their most favorable conformations to the active site due to steric interactions. PCBs lack the ether linkage connecting the phenyl rings and are classified as dioxin or non-dioxin-like based on ortho-substitutions. These two conformations differ in terms of toxicity—non-dioxin-like PCBs are only toxic at higher concentrations (>1000 nM), while dioxin-like PCBs are highly toxic and mimic the structure of TCDD. Addition of halogens to ortho positions restrain the PCB to a noncoplanar conformation due to steric clashes, leading to lower flexibility around the central C-C bond [73]. Therefore, highly-ortho chlorinated species have much lower conformational flexibility, which may impact the ability of the PCB to adapt to the active site and inhibit the protein.
While these small models provide insight on the XB interactions in the active site of Dio, the simple model itself is insufficient for describing various factors that may influence overall XB favorability. Interactions with active site residues will control regioselective binding and activation of THs and the ability of inhibitors to block the active site. For example, OH-substituted inhibitors may be accommodated by the His-Arg clamp proposed for Dio3 [7]. The X···O and X···N XB interactions to ancillary halogens may increase the stability of the TH substrate in the active site. Hydroxylated PCBs and PBDEs that can interact with this clamp and form the X···Se interaction could be the most potent inhibitors. Experimental studies of Dio with PCBs, PBDEs and related xenobiotics are necessary to further explore the relationship between selectivity, inhibition, and substitution pattern.
From the modeling perspective, simulations of full proteins will be needed to understand how these factors affect the XB interaction and substrate binding. Force fields have been developed to account for XB interactions through the use of dummy atoms to represent the anisotropic density at the halogen [117,118,119,120,121]. In addition, AutoDock VinaXB has been developed to include a halogen bonding scoring function [122]. Calculating the free energies of binding (i.e., ΔG) may also be useful for predicting favorability of protein-ligand interactions. MMPBSA and MMGBSA (and their variants) and QM methods such as fragmented molecular orbital (FMO) could be used for such calculations and may aid in drug design for suitable inhibitors to target the active site of Dios [123,124,125]. Use of these computational methods to understand the underlying mechanisms and key interactions in Dios with an eye toward designing treatments for TH-related disorders is being pursued within our group.

Author Contributions

Conceptualization, E.S.M. and C.A.B.; investigation, E.S.M.; writing—original draft preparation, E.S.M.; writing—review and editing, C.A.B.; visualization, E.S.M.; supervision, C.A.B.; funding acquisition, C.A.B. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Institute of Health, grant number R15 GM119063-01A1.

Conflicts of Interest

The authors declare no conflict of interest.

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