UNLABELLED: 2-((2S,5R,8S,11S)-5-benzyl-8-(4-((2S,3R,4R,5R,6S)-6-((2-(4-(3-(18)F-fluoropropyl)-1H-1,2,3-triazol-1-yl)acetamido)methyl)-3,4,5-trihydroxytetrahydro-2H-pyran-2-carboxamido)butyl)-11-(3-guanidinopropyl)-3,6,9,12,15-pentaoxo-1,4,7,10,13-pentaazacyclopentadecan-2-yl)acetic acid ((18)F-RGD-K5) has been developed as an α(v)β(3) integrin marker for PET. The purpose of this study was to determine the biodistribution and estimate the radiation dose from (18)F-RGD-K5 using whole-body PET/CT scans in monkeys and humans. METHODS: Successive whole-body PET/CT scans were obtained after intravenous injection of (18)F-RGD-K5 in 3 rhesus monkeys (167 ± 19 MBq) and 4 healthy humans (583 ± 78 MBq). In humans, blood samples were collected between the PET/CT scans, and stability of (18)F-RGD-K5 was assessed. Urine was also collected between the scans, to determine the total activity excreted in urine. The PET scans were analyzed to determine the radiotracer uptake in different organs. OLINDA/EXM software was used to calculate human radiation doses based on human and monkey biodistributions. RESULTS: (18)F-RGD-K5 was metabolically stable in human blood up to 90 min after injection, and it cleared rapidly from the blood pool, with a 12-min half-time. For both monkeys and humans, increased (18)F-RGD-K5 uptake was observed in the kidneys, bladder, liver, and gallbladder, with mean standardized uptake values at 1 h after injection for humans being approximately 20, 50, 4, and 10, respectively. For human biodistribution data, the calculated effective dose was 31 ± 1 μSv/MBq, and the urinary bladder wall had the highest absorbed dose at 376 ± 19 μGy/MBq using the 4.8-h bladder-voiding model. With the 1-h voiding model, these doses reduced to 15 ± 1 μSv/MBq for the effective dose and 103 ± 4 μGy/MBq for the absorbed dose in the urinary bladder wall. For a typical injected activity of 555 MBq, the effective dose would be 17.2 ± 0.6 mSv for the 4.8-h model, reducing to 8.3 ± 0.4 mSv for the 1-h model. For monkey biodistribution data, the effective dose to humans would be 22.2 ± 2.4 mSv for the 4.8-h model and 12.8 ± 0.2 mSv for the 1-h model. CONCLUSION: The biodistribution profile of (18)F-RGD-K5 in monkeys and humans was similar, with increased uptake in the bladder, liver, and kidneys. There was rapid clearance of (18)F-RGD-K5 through the renal system. The urinary bladder wall received the highest radiation dose and was deemed the critical organ. Both whole-body effective dose and bladder dose can be reduced by more frequent voiding. (18)F-RGD-K5 can be used safely for imaging α(v)β(3) integrin expression in humans.
UNLABELLED: 2-((2S,5R,8S,11S)-5-benzyl-8-(4-((2S,3R,4R,5R,6S)-6-((2-(4-(3-(18)F-fluoropropyl)-1H-1,2,3-triazol-1-yl)acetamido)methyl)-3,4,5-trihydroxytetrahydro-2H-pyran-2-carboxamido)butyl)-11-(3-guanidinopropyl)-3,6,9,12,15-pentaoxo-1,4,7,10,13-pentaazacyclopentadecan-2-yl)acetic acid ((18)F-RGD-K5) has been developed as an α(v)β(3) integrin marker for PET. The purpose of this study was to determine the biodistribution and estimate the radiation dose from (18)F-RGD-K5 using whole-body PET/CT scans in monkeys and humans. METHODS: Successive whole-body PET/CT scans were obtained after intravenous injection of (18)F-RGD-K5 in 3 rhesus monkeys (167 ± 19 MBq) and 4 healthy humans (583 ± 78 MBq). In humans, blood samples were collected between the PET/CT scans, and stability of (18)F-RGD-K5 was assessed. Urine was also collected between the scans, to determine the total activity excreted in urine. The PET scans were analyzed to determine the radiotracer uptake in different organs. OLINDA/EXM software was used to calculate human radiation doses based on human and monkey biodistributions. RESULTS: (18)F-RGD-K5 was metabolically stable in human blood up to 90 min after injection, and it cleared rapidly from the blood pool, with a 12-min half-time. For both monkeys and humans, increased (18)F-RGD-K5 uptake was observed in the kidneys, bladder, liver, and gallbladder, with mean standardized uptake values at 1 h after injection for humans being approximately 20, 50, 4, and 10, respectively. For human biodistribution data, the calculated effective dose was 31 ± 1 μSv/MBq, and the urinary bladder wall had the highest absorbed dose at 376 ± 19 μGy/MBq using the 4.8-h bladder-voiding model. With the 1-h voiding model, these doses reduced to 15 ± 1 μSv/MBq for the effective dose and 103 ± 4 μGy/MBq for the absorbed dose in the urinary bladder wall. For a typical injected activity of 555 MBq, the effective dose would be 17.2 ± 0.6 mSv for the 4.8-h model, reducing to 8.3 ± 0.4 mSv for the 1-h model. For monkey biodistribution data, the effective dose to humans would be 22.2 ± 2.4 mSv for the 4.8-h model and 12.8 ± 0.2 mSv for the 1-h model. CONCLUSION: The biodistribution profile of (18)F-RGD-K5 in monkeys and humans was similar, with increased uptake in the bladder, liver, and kidneys. There was rapid clearance of (18)F-RGD-K5 through the renal system. The urinary bladder wall received the highest radiation dose and was deemed the critical organ. Both whole-body effective dose and bladder dose can be reduced by more frequent voiding. (18)F-RGD-K5 can be used safely for imaging α(v)β(3) integrin expression in humans.
Authors: Ryogo Minamimoto; Mehran Jamali; Amir Barkhodari; Camila Mosci; Erik Mittra; Bin Shen; Frederick Chin; Sanjiv Sam Gambhir; Andrei Iagaru Journal: Eur J Nucl Med Mol Imaging Date: 2015-06-11 Impact factor: 9.236
Authors: Helen Su; Natalia Gorodny; Luis Felipe Gomez; Umesh B Gangadharmath; Fanrong Mu; Gang Chen; Joseph C Walsh; Katrin Szardenings; Daniel S Berman; Hartmuth C Kolb; Balaji K Tamarappoo Journal: J Nucl Cardiol Date: 2014-03-14 Impact factor: 5.952
Authors: Thomas Ebenhan; Isabel Schoeman; Daniel D Rossouw; Anne Grobler; Biljana Marjanovic-Painter; Judith Wagener; Hendrik G Kruger; Mike M Sathekge; Jan Rijn Zeevaart Journal: Mol Imaging Biol Date: 2017-06 Impact factor: 3.488