Abstract
The liver hormone hepcidin regulates systemic iron homeostasis. Hepcidin is also expressed by the kidney, but exclusively in distal nephron segments. Several studies suggest hepcidin protects against kidney damage involving Fe2+ overload. The nephrotoxic non-essential metal ion Cd2+ can displace Fe2+ from cellular biomolecules, causing oxidative stress and cell death. The role of hepcidin in Fe2+ and Cd2+ toxicity was assessed in mouse renal cortical [mCCD(cl.1)] and inner medullary [mIMCD3] collecting duct cell lines. Cells were exposed to equipotent Cd2+ (0.5–5 μmol/l) and/or Fe2+ (50–100 μmol/l) for 4–24 h. Hepcidin (Hamp1) was transiently silenced by RNAi or overexpressed by plasmid transfection. Hepcidin or catalase expression were evaluated by RT-PCR, qPCR, immunoblotting or immunofluorescence microscopy, and cell fate by MTT, apoptosis and necrosis assays. Reactive oxygen species (ROS) were detected using CellROX™ Green and catalase activity by fluorometry. Hepcidin upregulation protected against Fe2+-induced mIMCD3 cell death by increasing catalase activity and reducing ROS, but exacerbated Cd2+-induced catalase dysfunction, increasing ROS and cell death. Opposite effects were observed with Hamp1 siRNA. Similar to Hamp1 silencing, increased intracellular Fe2+ prevented Cd2+ damage, ROS formation and catalase disruption whereas chelation of intracellular Fe2+ with desferrioxamine augmented Cd2+ damage, corresponding to hepcidin upregulation. Comparable effects were observed in mCCD(cl.1) cells, indicating equivalent functions of renal hepcidin in different collecting duct segments. In conclusion, hepcidin likely binds Fe2+, but not Cd2+. Because Fe2+ and Cd2+ compete for functional binding sites in proteins, hepcidin affects their free metal ion pools and differentially impacts downstream processes and cell fate.
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Introduction
Synthesis and secretion of the systemic iron-regulatory hormone hepcidin (rodent gene name Hamp1) by the liver is regulated by iron stores within macrophages, inflammation, hypoxia, and erythropoiesis (reviewed in Ganz and Nemeth 2012). Binding of circulating hepcidin to its target protein ferroportin-1 on enterocytes and macrophages leads to internalization and degradation of the hepcidin-ferroportin-1 complex by ubiquitination, thereby inhibiting the efflux of iron from intestinal enterocytes into the blood as well as preventing the release of stored iron from macrophages (Nemeth et al. 2004). Together, these effects result in a decrease in circulating iron levels.
The kidney has recently emerged as an organ with a significant role in systemic iron homeostasis (Thévenod and Wolff 2016). Substantial amounts of iron are filtered by the kidney and have to be reabsorbed to prevent iron deficiency. Accordingly, iron transporters and receptors for protein-bound iron are expressed in the nephron (reviewed in Martines et al. 2013; Smith and Thévenod 2009; Thévenod and Wolff 2016). Systemic iron overload induced by genetic diseases, such as hereditary haemochromatosis or β-thalassemia major result in renal iron deposition and kidney injury involving oxidative stress induced by the Fenton metal ion Fe2+ (Halliwell and Gutteridge 2015), various forms of cell death or inflammation (reviewed in van Swelm et al. 2020). It is intriguing that hepcidin is also locally expressed in various organs, including the kidney where it is found in the distal nephron, but not in the proximal tubule (PT) (Kulaksiz et al. 2005). Although several studies indicate that hepcidin protects against certain forms of kidney injury caused by oxidative stress (Scindia et al. 2015; van Swelm et al. 2016, 2018), and possibly interferes with cell death signaling or chelates Fe2+ (Farnaud et al. 2006, 2008; Gerardi et al. 2005), the function of hepcidin locally expressed in the distal nephron is not understood.
Cadmium (Cd2+) is a non-essential transition metal, which is taken up from the environment into the body through pulmonary and enteral pathways (Jarup and Akesson 2009). The kidney PT is a major target of Cd2+ toxicity by chronic (low) Cd2+ exposure (reviewed in Thévenod 2003, 2009). Renal dysfunction develops in up to 7% of the general population, and in its most severe form displays major features of renal Fanconi syndrome (Johri et al. 2010). Although Cd2+ is not a Fenton metal ion, it also increases cellular reactive oxygen species (ROS) formation, e.g., by disrupting ROS metabolizing enzymes (reviewed in Cuypers et al. 2010), which alters their anti-oxidative redox signature and leads to apoptotic and/or necrotic cell death, as happens in PT cells (Nair et al. 2015). The renal medulla also accumulates significant amounts of Cd2+ in humans and concentrations of Cd2+ can reach ~ 50% of the levels found in the cortex (Nagamine et al. 2007; Torra et al. 1994; Wang et al. 2009; Yoshida et al. 1998), although nephrotoxicity is less apparent (Johri et al. 2010). Cd2+ has similar bioinorganic chemical characteristics as Fe2+, and it can displace Fe2+ from its physiological binding sites (including Fe2+ transporters) to disrupt cellular functions and cause damage (reviewed in Moulis 2010). Indeed, the distal nephron expresses a variety of Cd2+ entry pathways, including iron response element (IRE)-regulated Fe2+ transporters (reviewed in Smith and Thévenod 2009; Thévenod and Wolff 2016).
Consequently, we assessed roles of hepcidin in Fe2+- and Cd2+-induced ROS formation and cell injury in the mouse kidney cortical and inner medullary collecting duct (CD) cell lines mCCD(cl.1) and mIMCD3.
Materials and methods
Experimental solutions
A CdCl2 stock solution (Merck; cat. # 2011; 2.5 mM dissolved in ddH2O) was used throughout the study and diluted 1:500–1:1000 in serum-free medium. Iron salts and Na+-ascorbate stock solutions were freshly prepared for each experiment. Stock solutions were as follows: FeSO4 (Sigma-Aldrich; cat. # F8048) or FeCl3 (Sigma-Aldrich; cat. # 157740), 5 mM in ddH2O or in 500 mM Na+-ascorbate, pH 7.4 where ascorbic acid (C6H8O6) (Sigma-Aldrich; cat. # A5960) was dissolved in ddH2O, pH titrated to 7.4 with 1 M NaOH and final volume adjusted to obtain a 500 mM stock solution. Stock solutions of iron salts and Na+-ascorbate were diluted 1:50 or 1:100 in serum-free medium for individual experiments. Stock solutions of 10 mmol/l desferrioxamine mesylate salt (Sigma-Aldrich; cat. # D9533) dissolved in phosphate-buffered saline (PBS) were freshly prepared prior to use.
Cell culture
The immortalized mouse kidney medulla CD cell line mIMCD3, was obtained from ATCC (cat. # ATCC CRL-2123). The mCCD(cl.1) cell line clone was originally derived from primary cultures of cortical CD microdissected from mouse kidney (Gaeggeler et al. 2005) and was obtained from Dr. Edith Hummler (University of Lausanne, CH). WKPT-0293 Cl.2 cells, an immortalized cell line from the S1 segment of rat PT, was obtained from Dr. Ulrich Hopfer (Case Western, Reserve University, Cleveland, OH, USA) (Woost et al. 1996). mIMCD3 cells were cultured in Dulbecco’s modified Eagle’s medium (DMEM)/nutrient mixture F-12 (1:1) (GibCo; cat. # 31330) supplemented with 10% fetal bovine serum (FBS) (Gibco; cat. # 10270-106), 50 U/ml penicillin, and 50 μg/ml streptomycin (Gibco; cat. #15140-122). mCCD(cl.1) cells were cultured in DMEM/F-12 (1:1) supplemented with 5% FBS, 100 U/ml penicillin, and 100 μg/ml streptomycin, 0.9 μmol/l insulin (Sigma–Aldrich; cat. # I1882), 5 μg/ml apo-transferrin (Sigma-Aldrich; cat. # T2252), 10 ng/ml EGF (Sigma-Aldrich; cat. # E9644), 1 nM T3 (Sigma-Aldrich; cat. # T6397), and 50 nM dexamethasone (Sigma-Aldrich; cat. # D4902) (Fila et al. 2011). WKPT-0293 Cl.2 cells were cultured in medium essentially as previously described (Lee et al. 2005). All cell lines were used at passage numbers 20–40 and cultured in 25 or 75 cm2 standard tissue culture flasks (Sarstedt) at 37°C in a humidified 5% CO2 atmosphere and passaged twice a week upon reaching ~ 80–90% confluency.
Animals
Six- to eight-week-old C57BL/6 mice of either sex (Charles River Laboratories) were provided food and water ad libitum and maintained through a 12–12 h light–dark cycle in a climate-controlled environment. Animal handling and euthanasia were performed in accordance with the recommendations of German Ethical Guidelines for Laboratory Animals and the European Directive on the Protection of Animals used for Scientific Purposes (2010/63/EU). Protocols were approved by the Governmental Animal Ethics Committee of North-Rhine-Westphalia, Germany (Landrat Ennepe-Ruhr-Kreis, file number 32/7 from January 20, 2014) and the Institutional Animal Care and Use Committee of the University of Freiburg and the ethics committee of the City of Freiburg (authorization: X18/08C). All efforts were made to minimize the number of animals used and their suffering. Mice were anaesthetized with CO2 and/or sacrificed by cervical dislocation, and kidneys were immediately excised. For qPCR and immunoblotting, kidney cortex was grossly separated from medulla by surgery using a scalpel and razor blades.
Transient transfections
Transient transfection of Hamp1 siRNA or expression plasmid were performed according to manufacturers’ protocols. In brief, 100 nM mouse Hamp1 (Hamp1si) (Sigma-Aldrich; cat # EMU174481) or 100 nM control siRNA (ctrlsi) (Eurogentec, cat. # SR-CL000-005) was mixed with Lipofectamine RNAiMAX (Thermo Fisher Scientific) in Opti-MEM I (Gibco) and incubated for 5 min at room temperature (RT). For PCR analyses, 10–100 nM siRNA was used. For plasmid transfection, 0.5–1.25 µg mouse Hamp1 plasmid (Origene, cat. # MC211974) or control plasmid were mixed with Lipofectamine 2000 (Thermo Fisher Scientific) in Opti-MEM I and incubated for 10 min at RT prior to transfection in 0.5–1 ml culture medium. For Hamp1 gene silencing or overexpression, cells were exposed for 6 h to siRNA or plasmid solutions in fresh serum-free standard medium without antibiotics. Medium was then replaced by siRNA- and serum-containing or serum-free medium with antibiotics and cultured for up to additional 18 h (24 h in total with or without experimental treatments). For hepcidin immunofluorescence staining in mCCD(cl.1), a different protocol was used: after transfection with siRNA for 6 h in serum-free medium, cells were cultured for additional 18 h in standard serum-containing medium with antibiotics before exposure to serum-free medium for 6 h with or without Cd2+.
RNA extraction, cDNA synthesis and RT-PCR
Cells were plated and cultured for 24–48 h up to a confluency of 50% prior to treatments and/or transfection (as described above), harvested by scraping and subjected to isolation of total RNA and synthesis of cDNA as previously described (Betten et al. 2018). Cell numbers used for seeding and multiwell culture plate formats are summarized in Suppl. Table 1 for all cell lines and assays. RNA was isolated from mouse cortex and medulla tissue samples using High Pure RNA Tissue Kit (Roche; cat. # 12033674001) according to manufacturer’s protocol prior to cDNA synthesis. PCR reactions were performed using specific primers and cycling protocols (Table 1). Primers were designed using PrimerBLAST software (NCBI) and/or taken from the literature and synthesized by Eurofins Genomics. Gel documentation and densitometry analysis were performed using Image Lab Software version 5.2 (Bio-Rad Laboratories), with correction for loading by the housekeeping gene glyceraldehyde-3-phosphate dehydrogenase (Gapdh).
qPCR
Cells were grown to confluence, treated ± transfection (see above and Suppl. Table 1), harvested by scraping and subjected to RNA isolation and cDNA synthesis as previously described (Betten et al. 2018). Target sequences were amplified by qPCR, essentially as described (Betten et al. 2018), in a StepOnePlus Real-Time PCR System (Applied Biosystems), using KAPA SYBR FAST qPCR Master Mix Universal with high ROX reference dye (Sigma-Aldrich). The following primers were used for amplification: rat and mouse Hamp1, forward 5′-GCTGCCTGTCTCCTGCTT-3′, reverse 5′-TTACAGCATTTACAGCAGAAGAGG-3′ (Kanamori et al. 2014); mouse Hamp1, forward 5′-TTGCGATACCAATGCAGAAG-3′, reverse 5′-GGATGTGGCTCTAGGCTATGTT-3′ (van Swelm et al. 2016); rat and mouse Gapdh, forward 5′-AGGGCTCATGACCACAGT-3′, reverse 5′-TGCAGGGATGATGTTCTG-3′ (NCBI Primer-BLAST); mouse Gapdh, forward 5′-CGGCCGCATCTTCTTGTG-3′, reverse 5′-CCGACCTTCACCATTTTGTCTAC-3′ (NCBI Primer-BLAST); mouse Actb, forward 5′-CGTGCGTGACATCAAAGAGAA-3′, reverse 5′-GGCCATCTCCTGCTCGAA-3′ (Betten et al. 2018); mouse Cat, forward 5′-GCAGATACCTGTGAACTGTC-3′, reverse 5′-GTAGAATGTCCGCACCTGAG-3′ (El Mouatassim et al. 1999); rat Cat, forward 5′-GCGAATGGAGAGGCAGTGTAC-3′, reverse 5′-GAGTGACGTTGTCTTCATTAGCACTG-3′ (Limaye et al. 2003). Primers were used at 300 nM final concentration. The cycling conditions were activation at 95°C for 5 min followed by 40 cycles of 95°C for 3 s and 60°C for 30 s (56°C for mouse Cat and 58°C for rat Cat), with melt curve analysis to check amplification specificity. Gene expression levels were calculated according to the 2−∆Cq method relative to the sample with the highest expression (minimum Cq) (Bustin et al. 2009). The data obtained were corrected to the expression of two stable reference genes: Gapdh and Actb.
Surface biotinylation
Cell surface proteins were isolated using the Pierce™ Cell Surface Protein Isolation Kit (Thermo Fisher Scientific; cat. # 89881), with some modifications. After biotinylation and quenching, cells were disrupted by nitrogen pressure cavitation at 350 lb per square inch for 2.5 min in a cell disruptor (Parr Instrument Company) followed by centrifugation of the homogenate at 1000×g for 10 min to remove nuclei and cellular debris, and the resulting supernatant was centrifuged at 15,000×g for 15 min to remove mitochondria. The remaining membranes in the supernatant were pelleted at 100,000×g for 45 min, subjected to a 15 min wash with 250 mM KBr to remove membrane-associated proteins and enrich transmembrane proteins, and centrifuged again at 100,000×g for 45 min. The resulting pellet was resuspended in kit lysis buffer and isolation of biotinylated proteins was continued according to the manufacturer’s protocol. All procedures were carried out at 4°C.
Immunoblotting
Sodium dodecyl sulfate polyacrylamide gel electrophoresis (SDS-PAGE) and immunoblotting were essentially performed according to standard procedures using rapid semi-dry transfer (Bio-Rad Laboratories Trans-Blot Turbo). Homogenization of cells and mouse kidney cortex or medulla was performed by sonication (Branson 450 Digital Sonifier) in isosmotic sucrose buffer supplemented with protease inhibitor cocktail (Sigma-Aldrich). Homogenates were centrifuged for 5 min at 500×g to remove unbroken cells, and the supernatant was collected for determination of protein concentrations by the Bradford method, using bovine serum albumin (BSA) as standard (Bradford 1976). Samples were mixed with Laemmli buffer and heated for 5 min at 95°C [or for 15 min at 65°C for immunodetection of divalent metal transporter 1 (DMT1)] and subjected to SDS-PAGE and immunoblotted. Primary anti-catalase (cat. # ab209211 or cat. # ab16731; 1:2,000) and anti-β-actin (cat. # A5316; 1:20,000) antibodies were obtained from Abcam and Sigma-Aldrich, respectively. Anti-PARP (cat. # 9542; Cell Signaling Technology) was diluted 1:3000. Anti-calcium channel CaV3.1 (α1G) (Sigma-Aldrich; cat. # C2240) was diluted 1:400. A rabbit polyclonal anti-rat DMT1 directed against the peptide sequence MVLDPEEKIPDDGASGDHGDS (Ferguson et al. 2001) generated by ImmunoGlobe GmbH (designated 1102#3) detects all four major DMT1 isoforms and was used at a concentration of 0.5 μg/ml. Horseradish peroxidase-conjugated secondary antibodies were purchased from Jackson ImmunoResearch Europe Ltd and used at a dilution of 1:10,000. Immunoblots were developed using Immobilon ECL substrate (Millipore; cat. # WBKLS0500) and visualized on blue X-ray films (Carestream). Densitometry analysis was performed using FIJI/ImageJ software (Schneider et al. 2012).
Catalase assay
Cells were plated and cultured for 24 h up to a confluency of 50% prior to treatments and/or transfection, as described above (see Suppl. Table 1). Cells were harvested by scraping into PBS and collected by centrifugation at 2000×g for 1.5 min at 4°C. Catalase activity was determined using a Catalase Fluorometric Detection Kit (Enzo Life Sciences, Inc.; cat. # ADI-907-027) according to the manufacturer’s instructions. Cell pellets were resuspended in 55 µl of 1X reaction buffer and lysed by five freeze/thaw cycles. To fall within the standard curve range, samples were diluted to 0.25–1.0 µg protein. Samples were measured at λex 530 nm λem 590 nm in a Mithras LB 940 Multimode Microplate Reader (Berthold Technologies) by repeated measurements every minute for 10 min. Catalase activity was determined from the standard curve performed in each experiment.
Cell viability and cell death assays
Cells were plated and cultured for 24–72 h prior to treatments and/or transfection, as described above (see Suppl. Table 1). Cell viability was determined by the MTT test, as previously described (Lee et al. 2005). Trypan blue exclusion was used as a test for necrosis. Detached cells in the medium and adherent cells were collected, diluted 1:2 with 0.4% trypan blue and automatically counted (Countess II FL, Thermo Fisher Scientific). Apoptosis was detected using the APOSTRAND™ ELISA Apoptosis Detection Kit (Enzo Life Sciences, Inc.; cat. # BML-AK120) according to the manufacturer’s protocol. The APOSTRAND™ ELISA is based on the sensitivity of DNA in apoptotic cells to formamide denaturation and the detection of the denatured DNA with a monoclonal antibody to single-stranded DNA (ssDNA). Treatments were performed in FBS-free medium without phenol red. FBS-free medium without phenol red or PBS were used as negative controls whereas ssDNA included in the APOSTRAND™ ELISA served as a positive control.
Immunofluorescence microscopy
0.5–6 × 104 mIMCD3 or mCCD(cl.1) cells/cm2 were plated onto untreated or polylysine-treated glass coverslips in standard growth medium and stained 1–3 days later, essentially as described previously (Wolff et al. 2008). Unless otherwise indicated, all immunostaining procedures were performed at RT. In brief, cells were washed 2–3 times with Ca2+ and Mg2+ containing PBS, fixed with 2–4% paraformaldehyde (PFA) in PBS for 10–15 min, permeabilized with 0.1–0.5% Triton X-100 for 15 min (or 1% SDS for 5 min for hepcidin) and blocked with 1% bovine serum albumin in PBS (BSA-PBS) for 30 min. Cells were incubated with rabbit polyclonal anti-CaV3.1 (Sigma-Aldrich; cat. # C2240; 1:250) and diluted in BSA-PBS overnight at 4°C. Alternatively, coverslips were stained either for metallothionein (MT) with mouse anti-MT clone E9 antibody (Dako; cat. # M0639; 1:500) in BSA-PBS for 90 min, or with rabbit polyclonal anti-hepcidin antibody (Abcam; cat. #ab30760; 1:100) in BSA-PBS for 2 h. After washout of primary antibodies, coverslips were incubated with anti-mouse or anti-rabbit Alexa Fluor® 488-conjugated secondary antibody (Thermo Fisher Scientific; cat. # A-11029 or A-11008; 1:400–1:500) in BSA-PBS for 45–60 min at RT. Nuclei were counterstained with 0.8 μg/ml 2′-(4-ethoxyphenyl)-5-(4-methyl-l-piperazinyl)-2,5′-bi-1H-benzimidazole, 3HCl (H-33342) (Calbiochem) for 5 min, and coverslips mounted with DAKO fluorescence mounting medium (Dako).
Conventional fluorescence microscopy was performed using a Zeiss Axiovert 200M epifluorescence microscope (Carl Zeiss) equipped with Fluar 40x/N.A. 1.3 and 100x/N.A. 1.3 oil immersion objectives, a Sola SM II light engine (Lumencor), filters for Alexa Fluor® 488 (green) and H-33342 (blue) with excitation/emission wavelengths of 480 ± 20/535 ± 25 nm, and 360 ± 20/460 ± 25 nm, respectively, and a Cool-SNAP ES CCD camera (Roper Scientific) or a pco.panda 4.2 camera (PCO). Images were acquired at fixed exposure times at the focal plane of highest contrast and analyzed with MetaMorph software (Universal Imaging), as described elsewhere (Abouhamed et al. 2006), unless otherwise indicated. Confocal images were acquired using a TCS SP5 laser scanning confocal microscope (Leica) with a Plan-Apochromat 63x/N.A.1.4 oil immersion objective (Leica) and an argon (488 nm) laser and analyzed using LAS AF software.
Immunofluorescence staining of tissue sections
For immunostaining, kidneys were cut into pieces and fixed with PLP (periodate/lysine/paraformaldehyde) overnight. Subsequently, tissue was cryoprotected in 15% and 30% sucrose, frozen in liquid nitrogen, and cut into 10 µm cryosections. Cryosections were washed with PBS, treated with 1% SDS/PBS for 5 min, blocked with 1% BSA-PBS for 15 min at RT and incubated with primary anti-catalase rabbit antibody (Abcam; cat. # ab209211; 1:1,000) in blocking solution overnight at 4°C. After washing with PBS, slides were incubated with donkey anti-rabbit IgG Alexa Fluor 594 (Thermo Fisher Scientific; cat. # A-11012; 1:400) for 1 h at RT. Slides were washed with PBS and mounted with Fluoromount-G (Southern Biotech; cat. # 0100-20) for nuclear staining. Slides were viewed using a TCS SP8 confocal laser scanning microscope with Plan-Apochromat CS2 20x/0.75NA IMM or CS2 40x/1.30NA oil immersion objective (Leica) and an OPSL (552 nm) laser.
Detection of ROS formation using CellROX™ green
mIMCD3 cells were plated on glass coverslips and cultured for 72 h up to a confluency of 80% prior to treatments and/or transfection, as described above (see also Suppl. Table 1). Cells were incubated with 5 µM CellROX™ Green reagent (Thermo Fisher Scientific; cat. # C10444) for 30 min at 37°C. After washing with PBS containing Ca2+/Mg2+, cells were fixed with 3.7% PFA for 15 min at RT, washed with PBS, nuclei were counterstained with 0.8 μg/ml H-33342 for 5 min, and coverslips were mounted with DAKO fluorescence mounting medium. Images were acquired with fixed exposure times at the focal plane of highest contrast and were analyzed with MetaMorph, as described above.
Quantification of fluorescence images
Quantification of fluorescence images was carried out using FIJI/Image J (Schindelin et al. 2012) or MetaMorph software, as described previously (Wolff et al. 2006). In brief, intensity thresholds were set to exclude cell-free regions. The mean fluorescence intensity per image was divided by the number of nuclei in the image to obtain average cellular fluorescence intensity. To correct for endogenous auto-fluorescence, intensity of negative control images, i.e., cells stained without primary antibody, was subtracted from all mean values.
Statistics
Unless otherwise indicated, the experiments were repeated at least three times with independent cultures. Statistical analyses were performed with GraphPad Prism v. 5.01 software (GraphPad Software Inc.) and all data sets were tested for parametric/non-parametric distribution. Bar diagrams showing means ± SD were used for parametric data sets and box plots presenting 25 and 75 percentiles and median (horizontal line) for non-parametric data sets, unless otherwise indicated. Statistical comparison between two groups was performed using Student’s unpaired t-test or Mann–Whitney test, if groups were parametric or non-parametrically distributed, respectively. If more than two parametric groups were compared, one-way ANOVA with Bonferroni post hoc test was applied, while Kruskal–Wallis test with Dunn’s post hoc test was used for non-parametric groups. Results with p < 0.05 were considered statistically significant.
Results
To investigate the role of hepcidin in Fe2+- and Cd2+-induced oxidative stress and damage at the cellular level, we first tested different rodent cell lines derived from several nephron segments. In rat PT [WKPT-0293 Cl.2; (Woost et al. 1996)], mouse cortical collecting duct (CCD) [mCCD(cl.1); (Gaeggeler et al. 2005)], and mouse inner medullary collecting duct (IMCD) [mIMCD3; (Rauchman et al. 1993)] cell lines, Hamp1 gene expression was measured using primer pairs common to mouse and rat Hamp1 (see qPCR Methods). The highest mRNA expression levels were detected in mIMCD3 cells (Suppl. Fig. 1), which aligns with hepcidin protein levels in different segments of the mammalian nephron (Kulaksiz et al. 2005).
When mIMCD3 cells were exposed to Cd2+ or Fe2+ for 24 h, both metal ions decreased cell viability, although with different potencies. Cd2+ displayed an EC50 of about 5 μmol/l, whereas Fe2+ was less potent with an EC50 of about 100 μmol/l (Fig. 1) (equimolar concentrations of Fe3+ had no effect). Interestingly, Cd2+ and Fe2+ at EC50 concentrations increased hepcidin expression of mIMCD3 cells at both the mRNA and protein expression level, as assayed by immunofluorescence microscopy (Fig. 2), suggesting an adaptive response to metal ion stress and death. Cd2+ (5 μmol/l) appeared to be more effective than 100 μmol/l Fe2+ because Cd2+ rapidly (46 h) induced hepcidin expression (Figs. 2a, 2c). In contrast, Fe2+ had no effect at 6 h but after 24 h showed a similar magnitude of induction as Cd2+ (Figs. 2b, 2d). Of note, use of ascorbate in the Cd2+ experiments (ascorbate was used to prevent oxidation to Fe3+ in the Fe2+ experiments) did not interfere with Hamp1 expression (123 ± 13% in 6 experiments, compared to respective Hamp1 expression with Cd2+ but without ascorbate) (data not shown).
To further clarify the role of hepcidin in cell injury induced by Cd2+ and Fe2+ in mIMCD3 cells, Hamp1 was effectively silenced by RNAi, as shown by complete eradication of Cd2+-induced upregulation of Hamp1 (Suppl. Figs 2a, 2b). Under these conditions, cell viability experiments were repeated in mIMCD3 cells. Surprisingly, Hamp1 silencing had opposite effects on toxicity of both metal ions after 24 h exposure: Cd2+ toxicity was reduced (Fig. 3a) whereas Fe2+ toxicity was exacerbated (Fig. 3b). As an endpoint of cell viability/death, the MTT assay does not discriminate between apoptosis, necrosis, or decreased proliferation. Therefore, we complemented these observations with specific tests for apoptosis and necrosis, which essentially confirmed the MTT data: Hamp1 silencing decreased both apoptosis (Figs. 3c, 3d) and necrosis (Fig. 3e) induced by Cd2+, whereas it increased necrosis in Fe2+-treated mIMCD3 cells (Fig. 3e). Transfection of a Hamp1 plasmid in mIMCD3 cells for 24 h increased Hamp1 expression by about twofold (Suppl. Fig. 2c) and had opposite effects on viability of mIMCD3 cells exposed to Cd2+ or Fe2+, when compared to Hamp1 silencing (see Figs. 3a, 3b): Hepcidin overexpression further increased Cd2+-induced but reduced Fe2+-induced cell death (Fig. 3f).
Hepcidin is protective against kidney cell injury associated with increased formation of ROS (Scindia et al. 2015; van Swelm et al. 2018). Furthermore, both Cd2+ and Fe2+ damage cells by inducing oxidative stress (reviewed in Cuypers et al. 2010; Dixon and Stockwell 2014). Hence, the role of hepcidin in oxidative stress elicited by Cd2+ and Fe2+ in mIMCD3 cells was investigated. As shown in Fig. 4a, both Cd2+ (2.5 μmol/l) and Fe2+ (50 μmol/l) increased ROS formation to a similar extent after 24 h exposure, as detected with CellROX™ Green. However, Hamp1 silencing decreased ROS production induced by Cd2+ whereas it increased ROS with Fe2+ exposure. Overexpressing hepcidin in mIMCD3 cells augmented Cd2+- but abolished Fe2+-induced ROS formation (Fig. 4b). ROS measurements mirrored MTT cell viability data (Fig. 3), indicating that Cd2+- and Fe2+-induced oxidative stress mediates cell death in mIMCD3 cells. Yet hepcidin had opposite effects on Cd2+- and Fe2+-induced ROS formation and consequent cell death, namely protection against Fe2+ but aggravation of Cd2+-mediated oxidative stress and death.
Hepcidin can chelate endogenous metal ions, in particular Fe2+ (Abbas et al. 2018; Farnaud et al. 2006, 2008; Gerardi et al. 2005). If so, the expression level of cellular hepcidin should determine the levels of endogenous redox active iron. This would explain the protective effects of hepcidin overexpression (Figs. 3f, 4b), and increased damage and ROS formation by Hamp1 silencing (Figs. 3b, 3e, 4a) in Fe2+-exposed cells. In contrast, opposite results obtained in Cd2+-exposed cells (Figs. 3a, 3c–f, 4a, 4b) make it unlikely that hepcidin also chelates Cd2+ in a similar manner to Fe2+. Cd2+ damages proteins and cells by competing with and displacing Fe2+ from various binding sites (reviewed in Moulis 2010). We therefore hypothesized that increased endogenous Fe2+ in Hamp1-silenced cells prevents its displacement by Cd2+ and cell injury (Figs. 3a, 3c–e). Conversely, decreased endogenous Fe2+ by hepcidin overexpression promotes Cd2+ displacement and cell damage (Fig. 3f).
To test this concept, the effect of exogenously added Fe2+ (50 μmol/l) was investigated on viability of control and Hamp1-silenced mIMCD3 cells exposed to Cd2+ (2.5 μmol/l, 24 h). Addition of Fe2+ increased cell viability of Cd2+ exposed cells transfected with control siRNA, but had no additional effect in Hamp1-silenced cells (Fig. 3g), suggesting a cellular mechanism protecting against Cd2+ toxicity that needs iron. We then performed the opposite experiment by depleting chelatable endogenous cellular iron with the iron chelator desferrioxamine (DFO) (Keberle 1964), which does not bind Cd2+ (Harrington et al. 2012). DFO (10 μmol/l) abolished the protective effect of Hamp1 silencing on Cd2+ damage (Fig. 3h), indicating that increased endogenous chelatable iron protects against Cd2+ damage in Hamp1-deficient cells. ROS formation induced by Cd2+ was also measured under conditions of exposure to exogenously added Fe2+ or DFO: addition of Fe2+ (50 μmol/l) decreased Cd2+-induced ROS formation in control cells, with no further effect by Hamp1 silencing (Fig. 4c). With DFO, Hamp1-silenced cells showed a significant increase of Cd2+-induced ROS formation, when compared to the respective controls without DFO (Fig. 4d).
ROS metabolizing enzymes require metal ions as co-factors for their activity. In contrast to superoxide dismutases and glutathione peroxidases, which are not iron-dependent (Halliwell and Gutteridge 2015), catalases are iron-dependent enzymes (Deisseroth and Dounce 1970) that convert hydrogen peroxide (H2O2) into oxygen and water (Ratliff et al. 2016). Strikingly, their activity is increased or reduced by high or low cellular iron, respectively (Deisseroth and Dounce 1970; Macdougall 1972; Schultze and Kuiken 1941; Srigiridhar and Nair 1998), and disrupted by Cd2+, which results in increased ROS formation with Cd2+ (reviewed in Cuypers et al. 2010). Deep sequencing of micro-dissected nephron segments from rodent kidney demonstrated catalase mRNA (Cat) is mainly detected in the S1-S3 segments of the PT, but significant levels of catalase can be detected in other nephron segments as well. In the CD, the highest expression was measured in the IMCD, although PT expression was about sixfold higher than in the IMCD (Lee et al. 2015). Expression of Cat mRNA by qPCR was ~ 2.5-fold higher in WKPT-0293 Cl.2 than in mIMCD3 cells (Suppl. Table 2), which was confirmed at the protein level by immunoblotting. The expression of catalase protein by immunofluorescence staining of mouse kidney sections (Suppl. Fig. 3a) as well as by immunoblotting of crudely separated mouse kidney cortex and medulla (Suppl. Fig. 3b) confirmed published differential expression measured in rodent cortical and medullar nephron segments at the mRNA (Lee et al. 2015) and protein levels (Muse et al. 1994). Moreover, catalase activity in rodent kidney cortex and medulla (Gonzalez-Flecha et al. 1993) correlated with mRNA expression levels [see above; (Lee et al. 2015)] and matched catalase activity in PT WKPT-0293 Cl.2 cells, which was approximately fourfold higher than in mIMCD3 cells (Suppl. Table 2).
The effect of Cd2+ on catalase function and the impact of exogenously added Fe2+ or DFO were investigated in mIMCD3 cells with or without Hamp1 silencing. As shown in Suppl. Fig. 4, except for Fe2+ increasing Cat mRNA, none of the experimental manipulations performed in this study significantly affected Cat mRNA expression. Yet exposure of cells to Cd2+ for 24 h strongly decreased catalase activity, whereas Fe2+ enhanced catalase activity (Fig. 5a), which confirms recent observations in plants (Biyani et al. 2019). The latter may be partly accounted for by the induction of Cat gene expression by Fe2+ (see Suppl. Fig. 4 and Piloni et al. 2016). Co-exposure with Fe2+ prevented the reduction of catalase activity induced by Cd2+. And Hamp1 silencing had the same protective effect as addition of Fe2+ (although neither Hamp1 silencing nor overexpression affected Cat mRNA levels; see Suppl. Fig. 4) on Cd2+-induced inhibition of catalase activity (Fig. 5a). DFO prevented the rescue of catalase activity by Hamp1 silencing in Cd2+-treated cells (Fig. 5b), which once more supports the concept that hepcidin binds iron (Farnaud et al. 2006, 2008; Gerardi et al. 2005).
Hepcidin is also detected in the cortical collecting duct (Gaeggeler et al. 2005), though at a lower level (Kulaksiz et al. 2005) (see also Suppl. Fig. 1). To ascertain whether reduced levels of hepcidin also interfere with endogenous redox active ion levels, key experiments were executed in a model system, namely the mCCD(cl.1) cell line, derived from mouse cortical collecting duct (see Suppl. Fig. 1). As shown in Fig. 6a, Cd2+ or Fe2+ for 24 h decreased cell viability in a concentration-dependent manner. Cd2+ was about ten times more toxic in mCCD(cl.1) cells (EC50 ~ 0.5 μmol/l) than in mIMCD3 cells, whereas Fe2+ displayed similar toxicity in both cell lines (EC50 of about 100 μmol/l) (see Fig. 1). Cd2+ and Fe2+ at EC50 concentrations increased hepcidin mRNA and protein expression in mCCD(cl.1) cells, which was prevented by transient transfection with Hamp1 siRNA (Fig. 6b–d and data not shown). Hepcidin silencing or co-exposure with Fe2+ reduced Cd2+, but not Fe2+ toxicity (Fig. 6e). These data further supported the hypothesis that hepcidin chelates protective Fe2+ in mCCD(cl.1) cells and that Fe2+ or Hamp1 silencing rescue catalase dysfunction elicited by Cd2+, which was confirmed by the experiments shown in Fig. 6f. This further underlines the validity of the model shown in Fig. 7 for all nephron segments (and possibly other tissues) expressing hepcidin.
Discussion
In the present study, we demonstrate distinct effects of hepcidin on Fe2+- and Cd2+-induced oxidative stress and death in mIMCD3 and mCCD(cl.1) cells (Fig. 7). Hepcidin protects against Fe2+-mediated oxidative cell injury but aggravates Cd2+-induced ROS formation and death (Figs. 3, 4).
Cd2+ is about 20–200 times more potent than Fe2+ to induce cell injury (Figs. 1, 3, 6a, 6e), ROS formation (Fig. 4), and hepcidin upregulation (Figs. 2, 6b–d) in mIMCD3 and mCCD(cl.1) cells. The different damaging potency of Cd2+ and Fe2+ could be explained by differences in the permeability of both metal ions in these cells as well as competition between Cd2+ and Fe2+ for uptake pathways in experiments where Cd2+ and Fe2+ were co-exposed. Two transport pathways that carry both Cd2+ and Fe2+ are expressed in rodent CD, namely DMT1 and the voltage-gated calcium channel CaV3.1 (α1G) (Andreasen et al. 2000; Ferguson et al. 2001; Wareing et al. 2003) (reviewed in Thévenod and Wolff 2016). The localization of these proteins was investigated in mIMCD3 cells in which most experiments in this study were performed. DMT1 was not detected among mIMCD3 surface proteins, as determined by surface biotinylation and immunoblotting (Suppl. Fig. 5a), thus excluding DMT1 as a relevant uptake pathway for Cd2+ and Fe2+. In contrast, the calcium channel CaV3.1 was expressed in mIMCD3 cells by immunofluorescence microscopy (Suppl. Fig. 5b, left) and mainly observed at the cell periphery, suggesting localization in the plasma membrane, which was confirmed by laser scanning confocal microscopy (Suppl. Fig. 5b, right) and surface biotinylation experiments (Suppl. Fig. 5c, arrow). CaV3.1 shows a lower permeability for Fe2+ compared to Cd2+ (Lopin et al. 2012a, b), which could well explain the higher potency of Cd2+ compared to Fe2+ (Figs. 1, 6a), but cannot be the reason for Cd2+ and Fe2+ co-exposure almost abolishing comparable levels of Cd2+or Fe2+ toxicity and oxidative stress (Figs. 3g, 4c, 6e).
The protein MT is upregulated by Cd2+ in the kidney (Sabolic et al. 2010) and protects against Cd2+ toxicity by its strong Cd2+ chelating (Freisinger and Vasak 2013) and anti-oxidative properties (Ruttkay-Nedecky et al. 2013), but it lacks iron binding properties (Waalkes et al. 1984). To exclude the possibility that Hamp1 silencing as well as increased or decreased endogenous iron might have altered the expression of MT, which would explain some of the observed Cd2+-induced changes of cell viability and ROS formation under those experimental conditions, immunofluorescence staining of endogenous MT was performed in mIMCD3 cells. Basal MT expression was low in mIMCD3 cells, while it increased by 5.5–8.3-fold (means of six experiments) upon exposure to 2.5 μmol/l Cd2+ for 24 h (Suppl. Fig. 6). In contrast, Hamp1 silencing, Fe2+ (50 μmol/l) or DFO (10 μmol/l) did not have any effect on MT expression (Suppl. Fig. 6). Hence, MT expression does not contribute to the observed effects of these experimental manipulations.
Several protective roles have been attributed to local (renal) hepcidin in the context of metal ion toxicity. Hepcidin protects against cell death induced by hemoglobin (van Swelm et al. 2016, 2018), reduces oxidative stress in murine ischemia/reperfusion acute kidney injury (Scindia et al. 2015), or chelates endogenous metal ions, including Fe2+ and copper (Abbas et al. 2018; Farnaud et al. 2006, 2008; Gerardi et al. 2005). All three mechanisms are consistent with the Fe2+, but not Cd2+, effects described in this study (see Figs. 3–6). However, both Fe2+ and Cd2+ damage mIMCD3 cells by oxidative stress (Figs. 3, 4). To reconcile these seemingly disparate results, we hypothesized that endogenous iron levels are crucial for catalase function and Cd2+ damages catalase by displacement of iron (Moulis 2010). As heme-containing enzymes, catalases require iron for their activity (Deisseroth and Dounce 1970), and iron deficiency decreases their activity in various tissues, including the kidney (Macdougall 1972; Schultze and Kuiken 1941; Srigiridhar and Nair 1998). Hepcidin upregulation increases binding of cellular iron (Farnaud et al. 2006, 2008; Gerardi et al. 2005), thus reducing the redox active labile iron pool (LIP) (Kakhlon and Cabantchik 2002) and cell stress induced by Fe2+ overload (Figs. 3f, 4b), but enhances Cd2+ toxicity by chelating endogenous iron that is required for the function of catalase (see Figs. 5, 6f).
Obviously, hepcidin appears to have no singular role in the cell (see above). Moreover, scavenging of ROS seems unlikely as a protective mechanism of hepcidin because ROS formation is increased by Cd2+ in mIMCD3 cells despite hepcidin upregulation (Fig. 2) and Cd2+-induced ROS formation is decreased by Hamp1 silencing (Fig. 4). Further, both systemic production of hepcidin as a liver hormone as well as tissue-specific expression as a local regulatory factor need to be considered to understand the manifold functions of hepcidin. In the kidney, hepcidin is not expressed in the PT but exclusively found in the distal nephron (Kulaksiz et al. 2005). There it appears to protect against iron overload by controlling luminal iron uptake via DMT1 downregulation, possibly involving an autocrine mechanism (Moulouel et al. 2013). Here we demonstrate an additional protective effect of intracellular hepcidin against iron overload in distal nephron cells. Hepcidin reduces ROS formation (Fig. 4) and cell death (Figs. 3, 6), likely through its role as an iron scavenger (Farnaud et al. 2006, 2008; Gerardi et al. 2005) thus decreasing cellular levels of the redox active LIP (Kakhlon and Cabantchik 2002). Hepcidin upregulation by Fe2+ (Figs. 2, 6b, 6d) could be an additional mechanism of protection of the distal nephron against iron damage; H2O2 is known to upregulate hepcidin in hepatocytes (Millonig et al. 2012), which could be the underlying mechanism accounting for hepcidin induction by Cd2+ and Fe2+. Systemic iron overload pathology mainly targets the PT in experimental animals (Richter 1980; Zainal et al. 1999) and humans (Landing et al. 1989; Pardo-Mindan et al. 1990) because the PT represents the preferential site of iron uptake, as it possesses the perfect machinery required for transepithelial iron reabsorption in the kidney (reviewed in Thévenod and Wolff 2016). Hence, lack of hepcidin expression in the PT (Kulaksiz et al. 2005) may be detrimental under conditions of increased PT iron reabsorption whereas catalase upregulation induced by iron (see Suppl. Fig. 4) would be protective, at least transiently.
Chronic Cd2+ exposure leads to accumulation of Cd2+ in various organs, in particular the kidney PT, because of the presence of major luminal uptake pathways for Cd2+ along with limited routes of basolateral exit and subsequent damage (reviewed in Prozialeck and Edwards 2012; Thévenod and Wolff 2016). MT is the major protective mechanism against Cd2+ toxicity in the PT and other tissues (reviewed in Klaassen et al. 2009). In addition, catalase is highly expressed in the PT (Lee et al. 2015; Muse et al. 1994), mainly in peroxisomes, but also in the cytosol (Kalmbach and Fahimi 1978; Litwin et al. 1988). Hence, disruption of PT catalase activity by both low iron and/or increased Cd2+ will favor dysfunction of the PT, but also the distal nephron, as shown in this study for mIMCD3 cells and mCCD(cl.1) cells. Interestingly, catalase activity in the three cell lines originating from different nephron segments [WKPT-0293 Cl.2 > mIMCD3 > mCCD(cl.1)] (see Suppl. Table 1) appears to inversely correlate with Cd2+ toxicity [WKPT-0293 Cl.2 < mIMCD3 < mCCD(cl.1)] (see Figs. 1, 6a and Nair et al. 2015). This is not the case for Fe2+ toxicity (see Figs. 1, 6a), suggesting that catalase activity is an important contributor to protection against Cd2+-induced damage of the kidney.
The absence of hepcidin in the PT could further protect against Cd2+ toxicity, as shown in Hamp1-silenced mIMCD3 cells and mCCD(cl.1) cells (Figs. 3a, 3c–e, 6e). Cd2+ also accumulates in the distal nephron (Nagamine et al. 2007; Torra et al. 1994; Wang et al. 2009; Yoshida et al. 1998). The lower catalase (Lee et al. 2015; Muse et al. 1994) and higher hepcidin expression levels (Kulaksiz et al. 2005) (which may be further upregulated by Cd2+; see Figs. 2a–c, 6b, 6c) enhance Cd2+-induced ROS formation and hence Cd2+ toxicity (see Figs. 3f, 4b). Why then is Cd2+ nephrotoxicity less pronounced in the medullary distal nephron (Johri et al. 2010)? Cellular Cd2+ entry pathways [i.e., entry pathways for essential metal ions, such as Fe2+, Zn2+, Mn2+, Ca2+ and their complexes with proteins or peptides; reviewed in (Thévenod et al. 2019)] are comparable between kidney cortex and medulla. The relative resistance of the distal nephron to Cd2+ toxicity may result from its lower sensitivity to oxidative stress (Campos et al. 1993; Gonzalez-Flecha et al. 1993). Thus increased adaptive responses by oxidative and other stress-induced processes must underlie less prominent Cd2+ toxicity in the distal nephron (Johri et al. 2010), Consequently, the distal nephron displays an increased potential for adaptive responses by oxidative stress-induced factors [e.g., hypoxia-inducible factor-1α (HIF-1α), neutrophil gelatinase-associated lipocalin (NGAL), to name a few (van Swelm et al. 2018; Zou and Cowley 2003)]. Furthermore, the metabolic profile in the medullary segments shows largely anaerobic glycolysis due to a low partial pressure for O2 (McDonough and Thompson 2012) along with lower abundance of mitochondria. This particular redox status could protect the kidney medulla from Cd2+-induced oxidative stress resulting from mitochondrial damage (Thévenod et al. 2020; Lee et al. 2020), although antioxidant enzyme activities are concomitantly decreased in the medulla compared to the cortex (Thiab et al. 2015).
If hepcidin plays a role in determining cellular iron levels, as supported by the current study, it is imaginable that physiologically hepcidin expressed in the distal nephron could regulate the activity of iron-dependent enzymes and functions, e.g., cellular metabolism, ATP production, ROS formation and/or signaling. Interestingly, the distribution of peroxisomal enzymes, including catalase, along the nephron correlates with that of mitochondria, a major source of cellular ROS formation, as well as of Na+/K+-ATPase activity (Guder and Ross 1984). Peroxisomes and mitochondria relate functionally, as evidenced by their communication, cooperation and division machinery (Vasko 2016). Thus, hepcidin in the distal nephron could aid to adjust the metabolic and transport demands of the distal nephron under conditions of low tissue O2 partial pressure, as encountered in the kidney medulla. This requires verification in future studies.
In summary, as studied in renal mIMCD3 and mCCD(cl.1) cells, hepcidin binds Fe2+ but not Cd2+. Because Fe2+ and Cd2+ compete for functional binding sites in proteins, hepcidin affects their respective free metal ion pools and impacts differently on downstream processes, such as ROS formation, catalase activity and cell fate (see Fig. 7).
Availability of data and materials
The datasets used and/or analyzed during the current study are available from the corresponding authors on reasonable request.
Code availability
Not applicable.
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Research related to this work was supported by the Deutsche Forschungsgemeinschaft (DFG TH345), a BMBF grant between Germany and Mexico (BMBF 01DN16039) and the Centre for Biomedical Training and Research (ZBAF) of the University of Witten/Herdecke.
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Probst, S., Fels, J., Scharner, B. et al. Role of hepcidin in oxidative stress and cell death of cultured mouse renal collecting duct cells: protection against iron and sensitization to cadmium. Arch Toxicol 95, 2719–2735 (2021). https://doi.org/10.1007/s00204-021-03106-z
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DOI: https://doi.org/10.1007/s00204-021-03106-z