Abstract
Non-invasive imaging techniques to dynamically map whole-body trafficking of essential metals in vivo in health and diseases are needed. Despite 62Zn having appropriate physical properties for positron emission tomography (PET) imaging (half-life, 9.3 h; positron emission, 8.2%), its complex decay via 62Cu (half-life, 10 min; positron emission, 97%) has limited its use. We aimed to develop a method to extract 62Zn from a 62Zn/62Cu generator, and to investigate its use for in vivo imaging of zinc trafficking despite its complex decay. 62Zn prepared by proton irradiation of natural copper foil was used to construct a conventional 62Zn/62Cu generator. 62Zn was eluted using trisodium citrate and used for biological experiments, compared with 64Cu in similar buffer. PET/CT imaging and ex vivo tissue radioactivity measurements were performed following intravenous injection in healthy mice. [62Zn]Zn-citrate was readily eluted from the generator with citrate buffer. PET imaging with the eluate demonstrated biodistribution similar to previous observations with the shorter-lived 63Zn (half-life 38.5 min), with significant differences compared to [64Cu]Cu-citrate, notably in pancreas (>10-fold higher at 1 h post-injection). Between 4 and 24 h, 62Zn retention in liver, pancreas, and kidney declined over time, while brain uptake increased. Like 64Cu, 62Zn showed hepatobiliary excretion from liver to intestines, unaffected by fasting. Although it offers limited reliability of scanning before 1 h post-injection, 62Zn-PET allows investigation of zinc trafficking in vivo for >24 h and hence provides a useful new tool to investigate diseases where zinc homeostasis is disrupted in preclinical models and humans.
Keywords: 62Zn, positron emission tomography, zinc trafficking, copper trafficking, PET metallomics, non-invasive imaging
Graphical Abstract
Graphical Abstract.
Imaging zinc trafficking in vivo with 62Zn-PET.
Introduction
With an estimated 10% of the human genome encoding zinc proteins,1 zinc homeostasis is vital for normal physiological function. Dysregulation in zinc trafficking has been reported in several diseases of high socio-economic impact, including cancer,2–6 Alzheimer's disease,7,8 and diabetes.9–11 In order to investigate the role that zinc trafficking plays in disease, a technique is required that can monitor these dynamic pathways in a non-invasive manner throughout the whole body in animals and humans. Inductively coupled plasma mass spectrometry (ICP-MS) and zinc-sensing fluorescent probes are powerful tools for quantifying endogenous zinc, but are limited to in vitro and invasively obtained ex vivo samples.12 Recent efforts have been made to adapt zinc-sensing contrast agents for in vivo use as medical imaging contrast agents to study zinc in vivo.13–16 These are potentially useful agents to study labile zinc pools, but tools providing complementary information on the dynamic flux of zinc within the body are lacking. Positron emission tomography (PET) is a non-invasive medical imaging technique that provides dynamic functional information on biological molecular processes by mapping positrons originating from radioactive isotopes. With positron-emitting radioisotopes of essential metals becoming increasingly available, PET imaging is emerging as a means of studying dynamic acute (real-time) trafficking of essential metals at the whole-body level.17,18 The metal most studied to date by this approach is copper,19–24 but positron-emitting radioisotopes of zinc have been sought recently for this purpose.25,26
Three radioisotopes of zinc have applications in studying zinc biology (Table 1). 65Zn has the longest half-life (t1/2 = 243.8 days), and has been used to investigate zinc absorption and metabolism in plants,27 rodents, and humans.28–30 Although it emits gamma photons and low-abundance positrons, it is not suitable for whole body in vivo imaging owing to its long half-life and consequent problems of high radiation absorbed dose, and difficult radioactive waste management; in vivo measurements with 65Zn are limited to biopsy of selected tissues and subsequent gamma counting, which require much smaller amounts of radioactivity than imaging. The favourable emission properties of 63Zn (β+, 93%) and short half-life (38.5 min) make it an excellent option for imaging short-term (< 2 h) zinc biodistribution.25,26 To study zinc trafficking for longer periods, a longer half-life positron emitter is needed.
Table 1.
Positron-emitting radioisotopes of zinc that have potential applications as tools for metallomics investigations
Radio nuclide | Half-life (t1/2) | Decay modea | Mean positron energy (MeV) | Daughter nuclide | Production method |
---|---|---|---|---|---|
62Zn | 9.3 h | β+(8.2%), EC | 0.26 | 62Cub | Cyclotron: solid Cu foil target, 63Cu(p,2n)62Zn |
63Zn | 38.5 min | β+(93%), EC | 0.99 | 63Cu | Cyclotron: liquid 63Cu nitrate target, 63Cu(p,n)63Zn |
65Zn | 243.8 d | β+(98%), EC | 0.14 | 65Cu | Cyclotron: solid 65Cu target, 65Cu(p,n)65Zn |
EC denotes electron capture. a Parentheses denote percentage intensity (I). b 62Cu decays via β+ decay (t1/2 = 10 min, Iβ+ = 98%, Eβ+ = 2.91 MeV).
62Zn, previously used as the parent radionuclide in 62Zn/62Cu generators as the basis of 62Cu-radiopharmaceutical production,31–34 has a suitable half-life (9.3 h) but due to its complex decay mode it has not seen significant use in PET imaging. Only 8.2% of 62Zn decays yield a positron. However, each decay of 62Zn yields the high-abundance positron emitter 62Cu (t1/2 = 9.7 min, β+, 98%). Thus, in an imaging experiment with 62Zn, after radioactive equilibrium is reached (about 1 h) more than 90% of the emitted positrons are from the daughter radionuclide 62Cu, raising the question of whether images reflect 62Zn distribution or redistribution following decay to 62Cu. An important distinction is that the half-life of 62Zn is greater than that of 62Cu by a factor of 60. Consequently, if an equilibrium mixture of 62Zn and 62Cu is injected into a subject, 1 h later six half-lives of 62Cu will have elapsed and essentially all the injected 62Cu will have decayed. Thereafter, on average, almost all the positrons detected will have been emitted by a radionuclide (62Cu or 62Zn) that has spent more than 98% of its existence since the time of injection as zinc rather than copper. Therefore, it is highly likely that the location of the decay event will represent the result of trafficking of zinc rather than copper and that in most biological settings, the short half-life of 62Cu will not allow sufficient time for significant redistribution following the in vivo conversion to 62Cu. We therefore hypothesized that, despite the perceived challenges, 62Zn will be a useful radionuclide with which to image zinc trafficking in vivo. Hence, we decided to re-evaluate PET imaging with 62Zn as an ‘in vivo generator’ of 62Cu, by direct comparison of 62Zn biodistribution with that of the copper radioisotope 64Cu.
Here we describe a new low-cost manually operated 62Zn/62Cu radionuclide generator system based on a published design,33 and its subsequent use to produce 62Zn in a form suitable for in vivo PET imaging, aiming to determine whether this underutilised radionuclide can provide insight into the dynamics of zinc trafficking in models of health and disease over a time period that cannot be achieved with the shorter half-life radioisotope, 63Zn. We report for the first time the biodistribution of zinc administered intravenously (i.v.) as zinc citrate over a period of 24 h, where previously only 2 h was possible because of the short half-life of 63Zn. We also investigated the effect of fasting on hepatobiliary clearance of 62Zn.
Methods
General
Reagents and materials were purchased from Sigma-Aldrich (Gillingham, UK) unless otherwise stated. All reagents were commercially available and used without further purification. Concentrated hydrochloric acid (37%, BP) and absolute ethanol were obtained from Merck Millipore (Nottingham, UK). Sodium chloride 0.9% for injection was obtained from Braun (Hessen, Germany). C18 light sample preparation cartridges (Waters, Elstree, UK) were conditioned with ethanol (10 ml), followed by water (10 ml) and air (10 ml). Accell Plus CM Plus cartridges (Waters, Elstree, UK) were conditioned with water (10 ml) and air (10 ml). Chromafix PS-OH− cartridges (800 mg, Macherey-Nagel, Germany) were conditioned with 2 M HCl (20 ml) and air (20 ml). Vygon lines and connectors were obtained from Lectro-cath Vygon (Swindon, UK). Unless otherwise stated, TraceSELECT water for trace analysis (Fluka) was used throughout. Data were exported and statistical analyses were performed using GraphPad Prism (v.9.0). All parameters were analysed by unpaired t-test, *, P < 0.05; **, P < 0.01; ***, P < 0.001; ****, P < 0.0001.
Production of 62Zn
A copper foil target (thickness 0.5 mm, diameter 1 cm, purity: 99.9%, purchased from Goodfellow Cambridge Ltd) was irradiated using an MC40 cyclotron (27 MeV protons, 35 µA for 9 h) at the School of Physics and Astronomy, University of Birmingham. Approximately 20 h after the end of bombardment, during which period radioimpurities such as 61Cu (t1/2 = 3.3 h) decayed substantially, the irradiated foil was transported to King's College London for extraction and purification of 62Zn as described below.
Purification of 62Zn and preparation of 62Zn/62Cu generator
Purification and preparation of the 62Zn/62Cu generator was performed in a heavily shielded hot cell. The irradiated copper foil (∼0.7 g) was placed in a shielded 250 ml glass bottle containing hydrogen peroxide (25 ml, 30%, Fluka) and a magnetic stirrer bar on a magnetic stirrer under a fume extractor (see Fig. S1). Concentrated HCl (25 ml, 37%), followed by water (50 ml), was added to the bottle at a flow rate of 3 ml/min using a Watson Marlow peristaltic pump. The mixture was stirred using the magnetic stirrer throughout the procedure. Upon complete dissolution of the target, the blue-green mixture was passed through a shielded pre-conditioned strong anion exchange PS-OH− cartridge driven by the negative pressure generated by a vacuum pump, and the eluate collected in a shielded waste bottle. The PS-OH− cartridge was washed with 2 M HCl (80 ml, via tube 1, Fig. S1) to remove the copper, followed by absolute ethanol (50 ml, through tube 1, Fig. S1) to remove excess acid remaining on the cartridge. The 62Zn/62Cu generator was prepared by eluting 62Zn from the PS-OH− cartridge with water (20 ml) and trapping it on a shielded, pre-conditioned hydrophilic cation exchange Sep-Pak Accell Plus CM Plus cartridge, while collecting the eluate in the shielded waste bottle. To remove all the radioactive and non-radioactive copper impurities from the cation exchange cartridge, glycine solution (105 ml, 200 mM in water) was passed through the cartridge into the waste bottle. At this stage, after a suitable induction period (∼20 min) to allow 62Zn to decay, 62Cu can be eluted repeatedly from the generator with further glycine washes and can be used to label a wide range of 62Cu radiopharmaceuticals. Elution details for 62Cu and subsequent radiolabelling of an exemplar radiotracer, [62Cu]Cu-ATSM, can be found in the supplementary information.
Elution of 62Zn from the 62Zn/62Cu generator
Once immediate needs for 62Cu elution had been met, 62Zn was eluted from the generator with 4% trisodium citrate (1 ml, 136 mM in water, pH 6). Initially, this was used without further modification for in vivo studies similar to those reported for 63Zn by DeGrado et al.25,26 However, the high concentration of citrate was not tolerated well by mice. Therefore, for in vivo studies [62Zn]Zn-citrate solution (100 MBq, 100 μl) was diluted 16-fold in saline to give a 62Zn solution with a final citrate concentration of 0.25% (8.5 mM), well below the tolerated limit in mice, and a volume of 1.6 ml.
Quality control of 62Zn
Verification of the radionuclidic purity was determined by gamma spectrometry using a ORTEC GEM Series High-Purity Germanium (HPGe) Coaxial Detector System coupled to a DSPEC jr 2.0 Digital Gamma-Ray Spectrometer. This system was calibrated in-house for energy and efficiency. Spectra were displayed and analysed with ORTEC GammaVision software (Version 6.01).
Production of 64Cu
64Cu was produced as previously reported35 in the form of copper-64 chloride ([64Cu]CuCl2) in 0.1 M HCl solution. [64Cu]CuCl2 (∼100 MBq, 200 μl) was concentrated to dryness under N2 at 100°C for 10 min and the residue dissolved in 0.25% trisodium citrate (1 ml) to give [64Cu]Cu-citrate at a final pH of 6.
PET/CT imaging
PET imaging was performed using a nanoScan-PET/CT (Mediso Medical Imaging Systems, Budapest, Hungary) system operating in list mode using 400–600 keV energy window and coincidence window of 1:3. CT scans were acquired for anatomical reference (55 keV X-ray, exposure time 1000 ms and 360 projections and pitch 1). PET projection data were reconstructed using the Tera-tomo® software package—a Monte Carlo-based fully 3D iterative algorithm with four iterations, six subsets, and 0.4 mm isotropic voxel size; corrections for attenuation, scatter, and dead-time were enabled. The data were then visualised and quantified using VivoQuant© (InviCro, Boston, USA) software. For 60-min scans, data were re-binned and reconstructed into a series of 1-min time frames for the first 5 min, 5-min time frames for the next 25 min and then 10-min time frames for the remainder of the 60-min scan period. For the 4 and 24 h scans, static 1-h images were reconstructed. For in vivo PET quantification, regions of interest (ROIs) were manually drawn over the brain, heart, liver, kidney, bladder, and thigh muscle. The CT images were used to define the boundaries of the organs. Given the large spillover of signal associated with 62Zn-PET between ROIs, care was taken to prevent this confounding organ uptake by avoiding regions where organs came into close proximity such as the liver and the apex of the heart. Time-activity curves were generated and expressed as percentage injected dose per gram of tissue (%ID/g). Area under the curve (AUC) for the regional TACs from 0 to 30 min (AUC0-30 min) and 30 to 60 min (AUC30-60 min) were calculated and compared between the radiometals.
PET imaging phantoms with 62Zn, 62Cu, 64Cu, and 18F
A NEMA-NU4 image quality (IQ) phantom (Fig. S5) was filled and imaged with 62Zn/62Cu (7.5 MBq), 62Cu (5.1 MBq), and 18F (3.7 MBq). This phantom has compartments for investigating the IQ metrics of noise, activity concentration recovery coefficient (RC, the ratio of activity concentration in small volumes to that of a uniform region), and count spillover into enclosed chambers filled with air or nonradioactive water. A PET scan was acquired for 20 min followed by a CT scan. Image uniformity was expressed as the percentage standard deviation (% STD) of radioactivity observed in an ROI accounting for 75% of the active diameter drawn in the centre of the fillable region of the phantom. To evaluate the RCs and their standard deviations (RCSTD), the concentrations of radioactivity at six transaxial slices were averaged for each of the five fillable rods and divided by the mean total phantom activity concentration. Spillover ratios (SOR) were determined by measuring the apparent radioactivity in the non-radioactive water (SORwater) and air-filled (SORair) chambers, divided by the mean total phantom activity concentration. Full width at half maximum (FWHM) was estimated by drawing several lines through a single point source from a 10 μl capillary tube (Jaytec, CAP-TF-10) and measuring the average distribution function. A second phantom, the Derenzo phantom, was used to visualise and compare spatial resolution of several different radionuclides by acquiring a 20-min PET scan followed by a CT scan. A similar radioactivity concentration was maintained for all PET radionuclides (∼1.5 MBq/ml).
In vivo PET imaging with [62Zn]Zn-citrate and [64Cu]Cu-citrate
All animal experiments were performed in accordance with the Animals (Scientific Procedures) Act, 1986 with protocols approved by the Animal Welfare and Ethical Review Body for King's College London (St Thomas’ Campus). Female BALB/c mice (9–11 weeks of age, n = 3–4 animals/group, Charles River Laboratories) were anaesthetised by isoflurane inhalation (3%, Animalcare, York, UK, in O2), cannulated via a tail vein and placed prone on the scan bed. A bolus of radiotracer (∼5 MBq, 150 μl) was then administered i.v. via a tail vein cannula. Animals were maintained under isoflurane anaesthesia (Isocare®, 1.5–2% in O2) at 37 °C, and vital signs monitored throughout the scan. A dynamic PET scan was continuously acquired from 0 min post-injection (p.i.) for 1 h followed by a 10-min CT scan. Animals were then allowed to recover from anaesthesia and were re-anaesthetised and re-scanned at 4 h and 24 h p.i. for 60 min. This scanning protocol was performed for [62Zn]Zn-citrate and [64Cu]Cu-citrate. An additional cohort of female BALB/c mice (9–11 weeks of age, n = 3) were fasted for 12–16 h, scanned dynamically for 60 min with PET after i.v. injection of [62Zn]Zn-citrate, followed by a 10-min CT scan.
Ex vivo biodistribution
Ex vivo biodistribution studies were performed in female (n = 4) and male (n = 4) BALB/c mice (9–11 weeks old) following an i.v. injection of [62Zn]Zn-citrate (∼0.7 MBq, 150 μl) or [64Cu]Cu-citrate (∼0.7 MBq, 150 μl) at both 1 h and 24 h p.i. The 24 h cohorts of mice in the female group were culled following the imaging protocol described above for both radiometals. The fasted cohort of mice was also culled for ex vivo biodistribution following the imaging protocol described above. All mice were culled via cervical dislocation, and tissues of interest were collected. All tissues were washed with phosphate-buffered saline (Sigma, 806552), blotted dry, weighed, and then counted using a gamma counter (1282 Compugamma; LKB, window set to channels 175–220; for the energy profiles see Fig. S4). Ex vivo biodistribution data were presented as %ID/g, where ID represents the total activity of all body parts excluding the tail.
Results
Production and purification of a 62Zn/62Cu generator
62Zn was produced using a high purity natural copper foil target via the 63Cu(p,2n)62 Zn nuclear reaction. A saturated yield of approximately 1.5 GBq/μA was achieved; 9 h bombardment at 35 μA produced approximately 28 GBq of 62Zn at the end of bombardment. Radioactive decay over 20 h left 6 GBq; the target was then shipped to King's College London for purification. The irradiated target material was dissolved in hydrogen peroxide and hydrochloric acid and purified by a conventional method described previously by Fukumura et al. to produce a hydrophilic cation exchange Sep-Pak Accell Plus CM Plus cartridge loaded with 62Zn.33 Glycine (200 mM) was used to elute the radioactive and non-radioactive copper from the 62Zn/62Cu generator column. After 60 min, the generator had regenerated and 62Cu was eluted with glycine. The eluted [62Cu]Cu-glycine solution was then used to produce [62Cu]Cu-ATSM to a GMP standard, with radionuclidic purity > 99% and radiochemical purity > 97% by radio--high performance liquid chromatography analysis (Fig. S3), described here as an exemplar as proof of principle for the use of a 62Zn/62Cu generator to synthesise 62Cu-labelled bis(thiosemicarbazone) radiopharmaceuticals for clinical use. The application of these ligands and others in PET has been summarised previously.34,36–39
After multiple elutions to produce 62Cu radiopharmaceuticals, or simply to remove the 62Cu if it was not required, the remaining parent 62Zn could then be eluted with trisodium citrate (1 ml, 136 mM in water, pH 6) providing [62Zn]Zn-citrate (∼300 MBq), with 99.6% radionuclidic purity by HPGe γ spectrometry (characteristic peaks of 62Zn at 549 keV and 596 keV; 0.4% 60Co, t1/2 = 5.3 years; Fig. S2) and overall purification yield of 73.0 ± 8.2% (n = 3), which could then be diluted in saline ready for i.v. administration to evaluate the potential use of 62Zn for PET imaging of zinc trafficking.
PET imaging phantoms with 62Zn, 62Cu, 64Cu, and 18F
PET images of the Derenzo phantom (Fig. 1) showed that capillary tubes filled with an equilibrated mixture of 62Zn/62Cu could not be resolved for the tube diameters tested. The largest rod diameter tested was 4.8 mm and thus spatial resolution was ≥ 4.8 mm for 62Zn/62Cu. 62Cu alone displayed even poorer resolution, while the more popular copper radioisotope 64Cu and the ubiquitous clinical standard radionuclide 18F both displayed superior resolution, resolving diameters ≥ 2.4 mm. FWHM of 5.4 mm and 1.5 mm for 62Zn/62Cu and 18F respectively were estimated from a 10 μl capillary tube at centre of field of view. Industry standard NEMA-NU4 IQ phantoms highlighted that both 62Zn/62Cu and 62Cu had ∼3-fold greater spillover ratio (SOR) in air than 18F, but their SOR values were similar in water (Fig. S6). Additionally, %SD was 1.7-fold and 2-fold higher for 62Zn/62Cu and 62Cu respectively compared to 18F indicating poorer image uniformity for these radionuclides.
Fig. 1.
PET images of Derenzo imaging phantoms with various PET radionuclides using a preclinical nanoPET scanner. Mean positron energy in MeV is displayed under each radionuclide. Rod diameters descending clockwise from lower left are 4.8, 4, 3.2, 2.4, 1.6, and 1.2 mm.
62Zn-PET in healthy mice compared with a 64Cu control
The biodistribution of [62Zn]Zn-citrate was investigated in vivo with PET imaging in female BALB/c mice at 0–1, 4, and 24 h p.i. (Fig. 2). The whole-body biodistribution generated from PET was then compared with [64Cu]Cu-citrate as a control to help distinguish the biodistribution of 62Zn from that of its daughter 62Cu present at the time of injection.
Fig. 2.
Dynamic PET/CT imaging of healthy mice after i.v. injection of [62Zn]Zn-citrate and [64Cu]Cu-citrate. Representative time course PET/CT maximum intensity projections of [62Zn]Zn-citrate (top) and [64Cu]Cu-citrate (bottom) post i.v. administration in female BALB/c mice (9–11 weeks old). (B = bladder, F = faeces, H = heart, I = intestines, K = kidney, L = liver, Lu = lungs, P = pancreas, and SG = salivary glands).
In mice given 62Zn, the majority of positron emissions at 1 h p.i. were observed from the heart, liver, kidneys, and intestines. Excretion was evident primarily via the hepatobiliary system. The biodistribution remained similar at 4 h, with decay-corrected activity gradually diminishing in organs over the next 20 h. By 24 h, as activity was excreted from the abdominal organs, the high radioactivity that had been present in pancreas but not readily discernible because of high abdominal background was more clearly evident. This biodistribution behaviour differed significantly at all imaging time points investigated from that of 64Cu injected in similar citrate buffer (as determined by PET) which at 4 and 24 h p.i. showed high activity in the liver, intestines, salivary glands, and kidneys, and elimination predominantly in the faeces and to a lesser extent in urine at early time points, but no obvious uptake in pancreas.
As in the phantom studies, the resolution of the mouse 62Zn/62Cu PET scans was inferior to that obtained with 64Cu. The 98% positron fraction of the daughter 62Cu (compared to just 8.2% with 62Zn) means 62Cu contributes most of the signal observed, and its high positron energy (2.91 MeV for 62Cu and 0.26 MeV for 62Zn, c.f. 0.27 MeV for 64Cu) causes relatively poor spatial resolution. These observations match those from 62Cu-PET investigations in the literature.36,40
To study the dynamic trafficking in more detail, PET data were segmented into bins to provide kinetic information on tissue uptake and clearance. Time-activity curves generated from the dynamic PET data are summarised in Fig. 3. Again, 62Zn and 64Cu differed substantially. 64Cu demonstrated an initial increase of activity in the kidneys in the first 2–3 min, followed by a decrease as radioactivity cleared to the urinary bladder. In contrast, after administration of 62Zn, while there was an initial accumulation of activity in the kidneys, this plateaued after 5 min and the majority did not clear to the bladder. Bladder, heart, liver, and muscle uptake over the first 5 min remained similar for both radiometals. However, a growing contribution from 62Zn with time, as well as distinct differences between copper and zinc handling, resulted in significant differences in uptake between radiometals. Uptake in the liver for both radionuclides plateaued after 10 min, and was significantly higher for 64Cu than for 62Zn (AUC30-60 min = 747.1 c.f. 423.4 respectively; P = 0.0405). 64Cu however showed faster clearance from the liver with a 39% reduction in activity from 1 to 4 h p.i. (36.1 ± 11.1 vs 24.6 ± 8.4%ID/g, respectively), compared to just 4% for 62Zn (20.6 ± 1.7 vs 19.9 ± 4.3%ID/g, respectively). A gradual decline in liver uptake was then seen over 24 h for both radiometals. In the first few minutes following i.v. administration, there was an exponential clearance of both radiometals from blood with an initial half-life of < 2 min followed by a phase in which clearance was too slow for estimation of the half-life up to 60 min. 62Zn uptake in the heart was greater than that of 64Cu (AUC30–60 min = 105.1 for 62Zn c.f. 57.5 for 64Cu, respectively; P = 0.0098). Uptake in the brain was low but detectable for both radiometals; however, 62Zn was higher (AUC30-60 min = 37.3 for 62Zn c.f. 14.5 for 64Cu, respectively, P = 0.0067). Brain 62Zn uptake increased 1.6-fold from 1 to 24 h p.i. (1.86 ± 0.41 vs 3.00 ± 0.80%ID/g, P = 0.0606) but brain 64Cu at 24 h remained the same as at 1 h (0.81 ± 0.09 vs 0.73 ± 0.20%ID/g, P = 0.5422). Given the combination of high spillover from surrounding abdominal organs, as well as the ill-defined, diffuse anatomy of the mouse pancreas which cannot be visualised with CT without exogenous contrast agents, quantifying pancreas uptake from the PET images was not possible and pancreatic activity was determined by ex vivo gamma counting of dissected organs.
Fig. 3.
62Zn and 64Cu display different in vivo behaviours. (A) Time-activity concentration curves (TACs) for [62Zn]Zn-citrate (●) and [64Cu]Cu-citrate (■) in major organs of interest. (B and C) Area under the time activity curve (AUC) for tissues at 0–30 min (B) and 30–60 min post injection (C). **, P < 0.005. Error bars represent 1 s.d. from the mean value (n = 3–4 animals) and in some cases are smaller than the symbols.
Ex vivo biodistribution
The ex vivo biodistribution of [62Zn]Zn-citrate and [64Cu]Cu-citrate at 1 and 24 h after i.v. injection was evaluated in female (Fig. 4) and male mice (Figs. S8 and S9) by weighing and gamma counting dissected organs. The results were consistent with the PET/CT images in all organs. [62Zn]Zn-citrate showed significantly (10-fold) higher pancreatic uptake compared to [64Cu]Cu-citrate at 1 h p.i. (30.90 ± 3.88 vs 3.03 ± 0.46%ID/g, P < 0.0001). Although there was some (∼60%) clearance of 62Zn from pancreas by 24 h, the high 62Zn:64Cu ratio in pancreas persisted. Uptake in the heart, spleen, kidney, bone and salivary glands was also significantly higher for 62Zn than 64Cu at 1 h p.i. Differences in bladder activity observed in the PET images are not evident in the ex vivo biodistribution at 1 h; however, significantly lower radioactivity was observed in the urine with [62Zn]Zn-citrate compared to [64Cu]Cu-citrate at 1 h p.i. (1.54 ± 1.46 vs 17.61 ± 5.00%ID/g, respectively, P = 0.0032). Given the time delay between collecting the organs and measuring them on the gamma counter, any 62Cu present in the urine at the time of culling would have since decayed. As observed during PET quantification, brain accumulation of 62Zn increased at 24 h compared to 1 h p.i. (1.39 ± 0.13 vs 0.95 ± 0.07%ID/g respectively, P = 0.0009). Additionally, 62Zn uptake in the brain was significantly higher than that of 64Cu at 1 h (0.95 ± 0.07 vs 0.57 ± 0.07%ID/g, respectively, P < 0.0001) and 24 h p.i. (1.39 ± 0.13 vs 0.53 ± 0.06%ID/g respectively, P < 0.0001). In male mice, 62Zn uptake increased 1.7-fold in the prostate and seminal vesicles from 1 to 24 h p.i. (1.19 ± 0.18 vs 1.98 ± 0.29%ID/g, respectively, P = 0.0035, Fig. S8) and was higher at both time points than 64Cu which decreased over this interval. Differences in biodistribution between genders were also observed (Fig. S10 for 62Zn, Fig. S11 for 64Cu). Higher brain, spleen, liver, and kidney uptake of 62Zn in female than in male mice was observed. Compared to males, greater accumulation of 64Cu was seen at 1 h p.i. in the stomach, intestines, kidneys, and brain of female mice. These gender-specific differences remained at 24 h. Reduced hepatic 64Cu uptake in female mice was observed at 1 and 24 h p.i., but was only statistically significant at 24 h p.i.
Fig. 4.
62Zn demonstrates significant differences in biodistribution compared to 64Cu. Ex vivo biodistribution of [62Zn]Zn-citrate and [64Cu]Cu-citrate in female BALB/c mice (n = 4) at 1 and 24 h after i.v. administration. Graphs represent mean ± SD. Comparisons were analysed for significance using an unpaired t-test, *, P < 0.05; **, P < 0.01; ***, P < 0.001; ****, P < 0.0001.
The effect of fasting on 62Zn biodistribution in mice over 1 h was investigated to see if biliary clearance into intestines is reduced. Reduced activity in the intestines would be beneficial for clinical PET investigations in the abdominal region. However, fasting animals for 14–18 h prior to 62Zn injection had no significant impact on the delivery of 62Zn from the blood to organs, or its retention in organs, including the liver, over a period of 1 h (see Fig. S12 for ex vivo biodistribution).
Discussion
A 62Zn/62Cu generator provides practical and reproducible access to short-lived 62Cu radiopharmaceuticals such as bis(thiosemicarbazone) complexes. Over the years, the properties of bis(thiosemicarbazone) complexes have been fine-tuned to provide a family of radiotracers, some designed as perfusion agents and others that provide a hypoxia-dependent PET signal. With the advent of total-body PET,41 the production of short-lived radiotracers, such as 62Cu, will bring new possibilities as they can be ‘multiplexed’ with other PET tracers to provide a more comprehensive assessment of diseases such as cancer. Similar generator-based systems to the one described here (Supplementary methods) have been used for many years to produce 62Cu,31–34 but little biological research has been performed with the parent radionuclide 62Zn. We have shown here that once the generator has met the demand for 62Cu production, elution of 62Zn can be reliably performed using trisodium citrate, producing a solution that can be diluted with saline and used directly for in vivo studies, without additional purification steps. Modifications to elute the 62Zn with different buffers is in principle possible to yield 62Zn in chemical forms other than citrate, but we have not yet evaluated this potential. Here, we aimed to investigate the whole-body biodistribution of [62Zn]Zn-citrate as a preliminary evaluation of its potential for imaging zinc trafficking in vivo, particularly over longer time periods than are possible with the previously reported studies with 63Zn PET, and to assess the extent to which interpretation of images would be confounded by the in vivo conversion to 62Cu, from which the vast majority (>90%) of positrons would originate. Our hypothesis was that, to a reasonable approximation, the PET images would reflect the biodistribution of 62Zn despite the PET signal originating largely from the daughter 62Cu. Two extreme scenarios can be envisaged. In one extreme, pure 62Zn is injected immediately after elution from the generator and before significant decay to 62Cu. This, of course, is likely to be unattainable in practice because radioactive equilibrium will be approached within a few minutes of the last elution of 62Cu. In this first scenario, the rapid initial deposition of radioactivity from blood into tissues means that the PET image reflects largely zinc. At the other extreme (more realistic in practice), an equilibrium mixture of 62Zn and 62Cu is injected. The low positron branching ratio (8.2%) and longer half-life (9.3 h) of 62Zn compared to 62Cu (98%, 9.7 min) means that >90% of the positrons from this mixture originate from 62Cu. Immediately after injection, the observed biodistribution therefore initially reflects the injected 62Cu, with a growing contribution from 62Zn over the next few minutes. Once the injected 62Cu has decayed (a process that is essentially complete by 1 h p.i., corresponding to six half-lives), the signal thereafter comes either directly from 62Zn decay (8.2%) or from 62Cu that has been formed in vivo, and the latter radioactivity has on average spent >98% of its existence in vivo as 62Zn (a consequence of the ratio of the half-lives of 9.3 h and 9.7 min). The rapid clearance of zinc from the blood,25,26 as seen with other essential metals such as copper22,23,42 and manganese,43,44 means that the majority of 62Zn decay would take place once it reached the tissue of interest. Only if the decay of 62Zn that has been deposited in its target tissue causes rapid redistribution of the daughter 62Cu (within a few minutes) and release from that tissue, will the image fail to reflect zinc trafficking to a reasonable approximation. We therefore proposed that over a period of up to 2 days, and with the exception of the first hour p.i., 62Zn is a useful option for studying zinc trafficking in vivo.
The biodistribution and imaging data described in this manuscript are consistent with this rationale. The ex vivo biodistribution of 62Zn (and its in vivo generated daughter 62Cu) at 1 and 24 h p.i. was compared with that of 64Cu (which is free of radioactive parent or daughter complications) in healthy mice, showing a significant difference in uptake of 62Zn and 64Cu in the liver, kidney, pancreas, salivary glands, spleen, and prostate/seminal vesicles. This is the first time, to our knowledge, that the biodistribution of 62Zn and 64Cu has been directly compared in vivo with PET. The profound differences seen between the 62Zn and 64Cu images provide evidence that the PET images post 1 h (and even pre-1 h to an extent) and biodistribution data reflect trafficking mainly of zinc and not copper.
Having drawn this conclusion, we are in a position to use our data to describe the trafficking of i.v.-injected zinc over a longer time period than was previously possible. The biodistribution of 62Zn is consistent with the previously observed biodistribution of 63Zn reported by DeGrado et al.25 with predominant uptake being observed in the pancreas, liver, kidney, intestines, and spleen. The results are in agreement with the essential role of zinc in the pancreas, where it mediates processing, storage, secretion, and action of insulin in pancreatic β cells,45,46 and in the prostate, where zinc inhibits aconitase resulting in the accumulation of citrate which may serve as a zinc ligand in prostatic secretion and in seminal fluid.4,47 What remains unknown is whether or not the acute delivery and distribution of radiometals matches bulk metal levels in the body accumulated over the subject's lifetime; this depends upon how rapidly the long- and short-term zinc pools (which will have both labile and inert components) equilibrate. Additional comparisons to ICP-MS measurements of total tissue zinc and copper content will be required in the future.
The major benefit of 62Zn compared to 63Zn is the ability to study zinc trafficking over several hours or days instead of 1–2 h. Imaging at 4 and 24 h p.i. showed excretion and redistribution that has not been observed previously with 63Zn, due to its short half-life. Notably, uptake in brain and prostate/seminal vesicles was significantly higher (∼2-fold) at 24 h compared to 1 h p.i. This indicates redistribution of zinc into these tissues from other organs over time. The activity in the majority of organs, particularly the liver and pancreas, decreases at 24 h but still remains prominent, suggesting some redistribution. Furthermore, significant radioactivity in the intestines suggests that the majority of Zn excreted from tissues is eliminated via faeces.
The dynamics of zinc trafficking has been modelled previously in rodents and humans28,48,49; however, the models were derived from studies where 65Zn was administered orally or subcutaneously, or used radioactive zinc in a form other than citrate. Intravenous administration as a delivery method bypasses some of the physiological metal trafficking routes, such as intestinal absorption and the first-pass liver uptake of radioactivity delivered by the hepatic portal vein. The long half-life of 65Zn allowed investigation of zinc kinetics for weeks.50 Oral administration resulted in lower %ID compared to our findings; this is expected because not all of the radioactivity is likely to be absorbed from the gut. Rapid kinetics of zinc uptake in tissues from the blood matched compartmental models derived from 65Zn biodistribution data. The large decrease of 62Zn observed in the liver, kidney, and pancreas at 24 h p.i. compared to 1 h p.i. agrees with turnover times previously reported. However, accurate turnover times for organs over a day, although feasible in principle with 62Zn, could not be determined from our preliminary data given the limited time points studied. Nevertheless, because of the availability and evident utility of 62Zn, PET now offers the opportunity to provide a comprehensive understanding of metal dynamics after various administration routes without the need to cull large numbers of groups of animals at predetermined time points.
A disadvantage of using 62Zn instead of 63Zn is that kinetics at early time points cannot be investigated quantitatively without correction by modelling the contribution of the daughter 62Cu. 62Cu present at the time of injection confounds early measurements (< 1 h). 64Cu data provides the information required to make this correction. Nevertheless, if blood dynamics or tumour kinetics over the first few minutes are needed, 63Zn is a much more suitable option. Also, the resolution of 62Zn/62Cu is poor in comparison to 63Zn, because of the high positron energy of 62Cu (2.91 MeV for 62Cu c.f. 0.99 MeV for 63Zn). This is a significant issue when imaging mice, as seen in Fig. 2, but is less problematic in humans. Post-processing methodologies such as image resolution recovery could be implemented here to improve the spatial resolution of 62Zn images, and are currently being validated. On the other hand, ex vivo biodistribution data are unaffected by the problem of spatial resolution, allowing us to quantitatively show similarity of 62Zn to 63Zn and their marked contrast to 64Cu—particularly in pancreas uptake and urinary excretion.
Interestingly, early urinary excretion was observed consistently with 64Cu but was much less with 62Zn. Kidney uptake was higher with 62Zn suggesting that the zinc is being reabsorbed and retained within the kidney rather than excreted. [64Cu]Cu-citrate displayed similar biodistribution to other ionic forms of copper (e.g. liver and intestinal uptake); however, renal excretion of 64Cu has not been reported as a major excretion pathway with other ionic forms of copper (dichloride and acetate).22,24,51 Citrate enhances early renal excretion, probably by forming a stronger complex with a more prolonged stability in vivo than the chloride or acetate forms, perhaps delaying transchelation to albumin sufficiently to allow glomerular filtration of the low-molecular weight copper complexes, whereas Cu administered as acetate or chloride very rapidly binds to albumin, which is not subject to glomerular filtration.24 This important observation demonstrates that radiometals administered in different weakly chelated forms can display different behaviour in vivo. Therefore, the choice of administration buffer should be carefully considered for the radiometal application. For example, 64CuCl2 has been used to image prostate cancer in clinical subjects51,52; in this context, [64Cu]Cu-citrate may not be an appropriate radiotracer for imaging prostate cancer as it could obscure the signal in the pelvic area due to urinary excretion. Establishing the effect different ionic speciation of radiometals has on their biodistribution is an important area for PET metallomics, as optimisation of the delivery of radiometals to tissues (tumours for example) could improve their diagnostic power.
Performing studies in both male and female mice was important to provide a base for future investigations in gender specific diseases, for example exploring the role of zinc as a biomarker in prostate cancer in men, or in breast cancer in women. The large body of evidence that supports the decline in endogenous zinc in prostate cancer compared to healthy prostate means that PET with radiozinc, as a largely diagnostic-focused tool in the clinic, has little benefit as radiozinc delivery is also likely to be reduced rather than increased in malignancy. This would lead to a hard-to-detect cold spot on a PET scan representing cancerous tissue, against a high background in surrounding healthy prostate tissue showing accumulation of radiozinc. The role of Zn in breast cancer is less clear than in prostate cancer but potentially as important. There is growing evidence that zinc is elevated in breast cancer (∼1.2- to 6.5-fold increase compared to stromal breast tissue).53–57 Moreover, zinc might be a useful biomarker for determining breast cancer subtype.57,58 Farquharson et al. demonstrated that oestrogen receptor positive (ER+) tumour samples had approximately 80% higher zinc concentrations than in oestrogen receptor negative (ER−) ones.58 This relationship could be studied further in vitro with radiozinc cell uptake studies and then in animals using PET imaging. Another exciting alternative is investigating the role of zinc in tamoxifen resistance. Taylor and co-workers have shown increased endogenous zinc in tamoxifen-resistant cells (using a Tam-R cell line established from MCF7 by chronic exposure to tamoxifen). The 2-fold increase in zinc was accompanied by a significant increase in expression of ZIP7—a zinc influx transporter thought to mediate uptake of zinc into the endoplasmic reticulum.59 Future experiments studying zinc in breast cancer with PET imaging might therefore be of significant value. Apart from breast cancer, imaging zinc could be useful for other disease states. Possible applications include imaging delivery and retention of zinc in diabetic pancreata, arthritic joints, Wilson's disease livers, and Alzheimer's disease brains.
Radionuclides, especially those with a long half-life (e.g., 65Zn), have long been important tools for metallomics research. Even without imaging, they have provided vital insight into metal dynamics from the cellular to the whole body level. However, without the advantages afforded by imaging, their use is limited; for example, large groups of animals must be culled at specific time points, each of which provides only a snapshot in time of metal distribution. Such studies are unfeasible in humans. PET metallomics as a non-invasive imaging paradigm aims to go beyond this, utilising positron-emitting radiometals to visualise metal kinetics and dynamics not just in selected organs but in all organs. The work described in this manuscript establishes 62Zn as a tool to study zinc trafficking dynamically on a whole-body level, and provides new data that goes beyond the early time points reported by DeGrado et al. for 63Zn.25,26 For example, the increased brain uptake at 24 h p.i. compared to 1 h p.i. may afford new insights into Alzheimer's disease that could not be studied previously with 63Zn.26 With expanding access to PET technology, 62 Zn and 63Zn can be harnessed to study zinc in vivo with PET to answer questions such as: What is the role different transporters play in Zn uptake and efflux? What effect does the local expression of these transporters have on zinc handling in vivo? How effective are novel chelator therapies at removing zinc from tissues, such as brain in Alzheimer's disease? Is there undesirable redistribution of the zinc after chelation therapy for copper overload in Wilson's disease? With the wealth of literature available on intracellular zinc handling, and the diverse range of preclinical models of systemic and localised transporter deficiencies recently reported, these tools are poised to make significant impact. For their full value to be realised, a collaborative approach is needed, bringing together imaging scientists, metal biologists, and inorganic chemists to exploit radiometal PET for the study of metal trafficking and clinical applications in trace metal-related disease.
Conclusions
The ability of 62Zn to image zinc trafficking on a whole-body scale in vivo has been demonstrated in this work. We have provided evidence that the PET images obtained after injection of 62Zn as its citrate complex reflect the trafficking in vivo primarily of zinc and not copper, despite potential complexity due to its in vivo decay to the positron emitter 62Cu. Similarly to 63Zn, which is free from such complications, 62Zn acutely localises to known zinc-rich organs such as the pancreas, kidney, prostate, and seminal vesicles. For example, [62Zn]Zn-citrate showed significantly higher (10-fold) pancreatic uptake compared to [64Cu]Cu-citrate at 1 h p.i. Although 62Cu present at the time of injection confounds early kinetic measurements in the first hour p.i., PET imaging with 62Zn provides an important quantitative tool that can be used to study zinc trafficking at later time points (up to 2 days), which was not possible with 63Zn (showing that liver, pancreas, and kidney uptake diminished, but brain uptake increased, at 24 h p.i.). Importantly, we have demonstrated new insights into how the body handles zinc differently compared to copper. Harnessing these PET tools will help in determining the role that metal trafficking plays in human health and disease and will be useful in preclinical models and human studies where metal homeostasis is dysregulated.
Supplementary Material
Acknowledgements
The authors thank Prof Wolfgang Maret (King's College London) for insightful scientific discussions. We acknowledge support from the Centre for Medical Engineering at King's College London funded by the Wellcome Trust and EPSRC (203148/Z/16/Z), the Wellcome Multiuser Equipment Radioanalytical Facility funded by Wellcome Trust (212885/Z/18/Z), and the EPSRC programme for Next Generation Molecular Imaging and Therapy with Radionuclides (EP/S019901/1, ‘MITHRAS’). ZY was supported by the NIHR Biomedical Research Centre award to Guy's and St Thomas’ NHS Foundation Trust in partnership with King's College London and King's College Hospital NHS Foundation Trust. GF was funded by the King's College London and Imperial College London EPSRC Centre for Doctoral Training in Medical Imaging (EP/L015226/1). FAS was supported by the CRUK City of London Centre Award [C7893/A26233]. JJB was supported by a studentship from the MRC Doctoral Training Partnership at King's College London. HEG was supported by Cancer Research UK. No other potential conflict of interest relevant to this article was reported.
Contributor Information
George Firth, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Zilin Yu, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Joanna J Bartnicka, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
David Parker, School of Physics and Astronomy, University of Birmingham, Edgbaston, Birmingham, B15 2TT, UK.
Jana Kim, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Kavitha Sunassee, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Hannah E Greenwood, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Fahad Al-Salamee, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Maite Jauregui-Osoro, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Alberto Di Pietro, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Joanna Guzman, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Philip J Blower, School of Biomedical Engineering & Imaging Sciences, King's College London, St Thomas’ Hospital, London, SE1 7EH, UK.
Data availability
The data underlying this article will be shared on reasonable request to the corresponding author.
Conflicts of interest
There are no conflicts to declare.
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Data Availability Statement
The data underlying this article will be shared on reasonable request to the corresponding author.