Lights and Shadows on the Sourcing of Silver Radioisotopes for Targeted Imaging and Therapy of Cancer: Production Routes and Separation Methods
Abstract
:1. Introduction
Radioisotope | Use | t1/2 | Decay Mode | Eβ− [keV] | Iβ− [%] | Eβ+ [keV] | Iβ+ [%] | Eγ [keV] | Iγ [%] |
---|---|---|---|---|---|---|---|---|---|
103Ag | PET | 65.7 min | ε + β+ (100%) | - | - | 2421 | 14.8 | 118.7 | 31.2 |
2688 | 8 | 148.2 | 28.3 | ||||||
2444 | 2.1 | 266.9 | 13.3 | ||||||
2156 | 1.6 | 1273.8 | 9.4 | ||||||
104gAg | PET | 69.2 min | ε + β+ (100%) | - | - | 2014 | 5.1 | 555.8 | 92.6 |
2197 | 4.1 | 767.6 | 65.7 | ||||||
2097 | 2.9 | 941.6 | 25.0 | ||||||
2955 | 2.0 | 925.9 | 12.5 | ||||||
104mAg | PET | 33.5 min | ε + β+ + IT (100%) | 3730 | 58.0 | 555.8 | 91 | ||
- | - | 2492 | 1.8 | 1341.7 | 1.6 | ||||
2944 | 1.1 | 767.6 | 0.9 | ||||||
111Ag | Therapy (+ SPECT) | 7.4 d | β− (100%) | 1035 | 92.0 | - | - | 342.1 | 6.7 |
694.7 | 7.1 | 245.4 | 1.2 | ||||||
791.4 | 1.0 |
2. Production of Silver-111
2.1. Reactor-Based Production
2.2. Accelerator-Based Production
2.2.1. Charged-Particle-Based Production
2.2.2. Photonuclear-Based Production
3. Production of Silver-103 and Silver-104m,g
3.1. Silver-103
3.2. Silver-104m,g
4. Separation of Silver Radioisotopes
4.1. Separation by Chemical Methods
4.1.1. Separation of Silver-111 from Palladium Targets
Chromatographic Methods
- Cation Exchange: Mansur et al. reported a cation-exchange-based chromatographic separation of 111Ag from the neutron-irradiated Pd matrix [21]. According to their protocol, the Pd target (100 mg) was dissolved in aqua regia (5 mL), followed by evaporation to dryness [21]. The process was repeated by adding HCl to remove residual amounts of HNO3 and the bulk was dissolved in distilled water (10 mL). Concentrated NH3 (25%, 7–8 mL) was then slowly added, and the resulting solution was warmed and passed through a column (1 cm diameter × 10 cm) filled with AG50W-X8 (50–100 mesh, H+ form, 5 g) pre-washed with water. A 1 mL/min flow rate was used throughout the process [21]. Silver and palladium cations were therefore adsorbed as [Ag(NH3)2]+ and [Pd(NH3)4]2+ complexes. After a washing step with water (20 mL), necessary to remove the excess of NH3, 111Ag-containing residue was eluted with a 0.5 M NaCl solution (16 mL, 80% yield) as [AgCl3]2−. Palladium was recovered by eluting the resin with 14 M HNO3 (80 mL). The concentration of Pd2+ in the 111Ag+ eluate was <1 μg/mL.
- Anion Exchange: Taylor et al. reported an anion-exchange-based separation [23]. After the irradiation (4–6 days, neutron flux = 1012 n/cm2/s), the palladium target was dissolved in aqua regia, and the resulting solution was evaporated to dryness. After heating, the residue was dissolved in a small volume of 10 M HCl to remove traces of HNO3 and passed into a column (1 cm diameter × 25 cm) filled with a Deacidite FF anion exchange resin. 111Ag-chloro complexes were eluted from the column with a subsequent rinse with 10 M HCl (50 mL). The solution was then evaporated to dryness and the residue dissolved in diluted HNO3, recovering 75% of the starting activity.
- Alumina Adsorption: Khalid et al. reported the possible use of alumina to adsorb the produced 111Ag and separate it from a neutron-irradiated palladium bulk matrix [28]. In their work, the irradiated Pd target (100 mg) was dissolved in aqua regia (5 mL) and the solution was evaporated to dryness. Repeated additions of concentrated HCl were performed to expel traces of HNO3 and the evaporation was carried out again. Then, the obtained residue was dissolved in 0.01 M HCl (30 mL) and the solution was passed at 1 mL/min through an alumina-containing column (5 g, 1 cm diameter × 10 cm) pre-conditioned with 0.01 M HCl. The column was washed with 0.1 M HCl (60 mL) to remove Pd2+ and the 111Ag-labelled residue was eluted with 4 M HCl (30–40 mL). More than 80% of the 111Ag-fraction was recovered in 20 mL and the palladium concentration was estimated to be <1 μg/mL.
Liquid/Liquid Extraction
Precipitation
- Precipitation as silver chloride: Collin et al. reported the dissolution of an irradiated palladium wire in hot concentrated HNO3 spiked with one drop of HCl [31]. Radioactive silver was then co-precipitated with an amount of stable AgNO3, inserted to increase the total mass of silver, by the addition of NaCl. Filtration allowed the recovery of AgCl, which was then dissolved in NH3 solution and reduced back to metallic silver by using ascorbic acid.
- Co-precipitation with mercury(I) chloride: Haymond et al. reported the separation of radioactive silver radioisotopes (105Ag, 106Ag and 111Ag) produced by bombarding a palladium target with 19 MeV deuterons (200 μA/h, average beam intensity 20 μA) through a precipitation technique using mercury(I) chloride as co-precipitant [16]. After the bombardment, the irradiated surface of the palladium target (approximately 0.5 g of Pd) was milled off and dissolved in aqua regia. The solution was evaporated to dryness and dissolved in 0.5 M HCl (500 mL) containing 50 mg of rhodium and ruthenium hold-back carrier. Then, a saturated solution of HgNO3 (0.5 mL) was added and the mixture was vigorously stirred. The precipitate of Hg2Cl2, containing over 95% of the radioactive silver, was centrifuged, washed with 0.5 M HCl and dissolved in the minimum needed volume of 16 M HNO3 [16]. Na2SO4 (200 mg) was then added, and the solution was evaporated to dryness (450 °C, 2 h) to drive off the mercury carrier. The residue was quantitatively solubilized in distilled water (10 mL) to give an isotonic saline solution of radioactive silver.
Co-Crystallization
Electrodeposition
Other Techniques
4.1.2. Separation of Silver-111 from Other Targets or Contaminants
- Separation of 111Ag from Th target: Mastren et al. reported the recovery of 111Ag from a proton-irradiated thorium matrix using a solvent-impregnated CL resin composed of alkyl phosphine sulfides and alkyl phosphine oxides [1]. The author proposed two methods, both of them involving the dissolution of the irradiated thorium target (10 g) in a mixture of 10 M HCl (200 mL) and 2 M HF (0.1 mL) by heating at 80–90 °C for 2 h. Then, in the first method (Figure 11), an aliquot of the dissolved target (0.1 mL) was diluted with 0.1 M HNO3 (5 mL). Subsequently, 50 μL of the obtained solution was diluted with 10 M HCl (5 mL) and passed through a column containing the preconditioned (10 M HCl) CL resin (1 mL). 225Ac produced from irradiation and the bulk Th target were not retained by the resin, whilst 111Ag was blocked and then eluted by using 10 M HNO3 (5 mL).
- Separation of 111Ag from 111Cd: Stable 111Cd is the main isobaric contaminant remaining when 111Ag is obtained via the isotope mass separation on-line technique (ISOL—vide infra). To efficiently separate Ag+ from Cd2+ and selectively harvest 111Ag, Tosato et al. employed an extraction chromatographic resin (CL resin) [37] and developed three alternative separation methods. In the first one, upon the loading of the resin, Cd2+ was quantitatively removed in the washing step (0.1 M HNO3) whereas Ag+ was firstly retained and subsequently eluted with 10 M HNO3. The reported recovery yield was 90 ± 5% [37]. In the second separation method, 7 M NH3 was used to quantitatively elute Ag+ instead of 10 M HNO3. Finally, 1 M H2SO4 was employed in the washing step of the third method to selectively remove Cd2+, while the elution of Ag+ was conducted using 0.1 M thiourea (yield 92%). Although these methods hold promise in depleting Cd contamination from ISOL-produced 111Ag, they have yet to be tested using irradiated samples.
4.2. Mass Separation Method
5. Final Remarks and Future Perspectives
6. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Isotope | Natural Abundance [%] | Nuclear Reaction and Final Product | Cross-Section [mb] |
---|---|---|---|
Palladium-102 | 1.02 | 180 | |
Palladium-104 | 11.14 | 75 | |
Palladium-105 | 22.33 | 217 | |
Palladium-106 | 27.33 | 29 | |
Palladium-108 | 26.46 | 868 | |
Palladium-110 | 11.72 | 340 |
Target Material | Produced Isotope | Threshold Energy [MeV] |
---|---|---|
Natural Cd | 111Ag | 9.6 |
105Ag | 7.3 | |
107Ag | 8.1 | |
109Ag | 8.9 | |
110mAg | 9.1 | |
112Ag | 9.7 | |
113Ag | 10.2 | |
115Ag | 11.0 | |
107Cd | 10.3 | |
109Cd | 9.9 | |
Natural In | 111Ag | 3.7 |
109Ag | 3.1 | |
114mIn | 9.0 | |
114Cd | 6.8 | |
112mIn | 9.4 | |
112Cd | 6.1 |
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Tosato, M.; Asti, M. Lights and Shadows on the Sourcing of Silver Radioisotopes for Targeted Imaging and Therapy of Cancer: Production Routes and Separation Methods. Pharmaceuticals 2023, 16, 929. https://doi.org/10.3390/ph16070929
Tosato M, Asti M. Lights and Shadows on the Sourcing of Silver Radioisotopes for Targeted Imaging and Therapy of Cancer: Production Routes and Separation Methods. Pharmaceuticals. 2023; 16(7):929. https://doi.org/10.3390/ph16070929
Chicago/Turabian StyleTosato, Marianna, and Mattia Asti. 2023. "Lights and Shadows on the Sourcing of Silver Radioisotopes for Targeted Imaging and Therapy of Cancer: Production Routes and Separation Methods" Pharmaceuticals 16, no. 7: 929. https://doi.org/10.3390/ph16070929
APA StyleTosato, M., & Asti, M. (2023). Lights and Shadows on the Sourcing of Silver Radioisotopes for Targeted Imaging and Therapy of Cancer: Production Routes and Separation Methods. Pharmaceuticals, 16(7), 929. https://doi.org/10.3390/ph16070929