Radiochemical separation and quality assessment for the 68Zn target based 64Cu radioisotope production Le Van So,* P.. The overlapped gamma-ray spectrum analysis method was developed to
Trang 1Radiochemical separation and quality assessment for the 68Zn target
based 64Cu radioisotope production
Le Van So,* P Pellegrini, A Katsifis, J Howse, I Greguric
Radiopharmaceutical Research Institute, Australian Nuclear Science and Technology Organisation,
New Illawarra Road, Lucas Heights , P.M.B 1, Menai NSW 2234, Australia
(Received July 31, 2007)
The radiochemical separation of the different radionuclides ( 64 Cu, 67 Cu, 67 Ga, 66 Ga, 56 Ni, 57 Ni, 55 Co, 56 Co, 57 Co, 65 Zn, 196 Au ) induced in the Ni supported Cu substrate – 68 Zn target system, which was bombarded with the 29.0 MeV proton beam, was performed by ion-exchange chromatography using successive isocratic and/or concentration gradient elution techniques The overlapped gamma-ray spectrum analysis method was developed to assess the 67 Ga and 67 Cu content in the 64 Cu product and even in the post- 67 Ga production 68 Zn target solution without the support of radiochemical separation This method was used for the assessment of 64+67 Cu radioisotope separation from 67 Ga , the quality control of
64 Cu product and the determination of the 68 Zn (p,2p) 67 Cu reaction yield The improvement in the targetry and the optimization of proton beam energy for the 68 Zn target based 64 Cu and 67 Ga production were proposed based on the stopping power and range of the incident proton and on the excitation functions, reaction yields and different radionuclides induced in the target system
Introduction
64Cu which emits both beta and positron in high
abundance (39% β– and 17.4% β+) with a half-life of
12.7 hours can play a role of bi-functional radioisotope
for both positron emission tomography (PET) imaging
and endoradiotherapy (ERT) The better physical
characteristics of low intensity of the high energy
gamma-ray (1345.7 keV, 0.47%) and low energy β+
-emission (653 keV) of 64Cu compared to 61Cu and 62Cu
are particularly useful for high resolution PET imaging
Its 578 keV energy β–-emission, nearly identical to that
of the 67Cu beta-emitter, is suitable for the ERT of small
tumours Besides, the electron capture decay with its
associated Auger emissions can yield more efficient cell
killing when the 64Cu nuclide is deposited in the cell
nucleus The combined effect of three decay modes of
the 64Cu radioisotope gives a high cell killing efficacy.1
64Cu’s preferable properties involved in
physiological pathways1–4 – being almost invariably
bound to protein or peptide for transport purposes and
for functional use, being sequestered in mettalothionein
as Cu(I)-thiolate clusters, the redox and electron/oxygen
transfer properties based enzymatic uses – make
radioactive copper complex molecules useful (in their
own right) as targeting radiopharmaceuticals (the
bis-[thiosemicarbazone] chelating group based PTSM and
ATSM complexes, porphyrins, bleomycin) These
compounds displaying the metal-essential biochemical
properties of Cu are being used for brain and myocardial
imaging studies (PTSM) and for tumour treatment
(PTSM and ATSM).1,3
Another use of the Cu radioisotopes is based on the
high capability of forming stable coordinative
complexes with bifunctional chelators1,2 – acyclic polyaminocarboxylate (DTPA, EDTA), cyclic polyamines (Cyclam) and macrocyclic polyamino-carboxylates (TETA, DOTA, NOTA) The last two groups of chelator–Cu complexes with good in-vivo stability make the Cu radioisotopes amenable to coupling with the targetted molecules such as peptides and antibodies for the in-vivo applications This type of Cu-bifunctional chelator-biomolecule-conjugate further offers more versatile applications in PET imaging and in targeting radiotherapy The 64,67Cu-chelator-antibody conjugates (MAb35-against carcinoembryonic antigen, SEN7 and SWA20-against lung cancer antigen, VG76e, B72.3 antibodies) are the best-known targeting radiopharmaceuticals to this date The 64Cu labeled ligands targeting receptors (64Cu-DOTA-[Pro1, Tyr4]-bombesin[1-14] for targeting GRP receptors, 64 Cu-TETA-somatostatin analogs, 64Cu-DOTA-Annexin V.,) are conjugates being widely investigated.1–5
Currently two cyclotron based methods are used for
64Cu production The first is based on the 68Zn target and second on 64Ni The 64Ni target based production process is recently developed and based on the
64Ni(p,n)64Cu reaction.3,5,8,11–14 This production route, which uses a proton beam energy lower than 13 MeV for activation, has the advantages of no side nuclear reactions which could induce radionuclidic impurities in the 64Cu product However, the disadvantage of this process is the use of very expensive enriched 64Ni target The larger cyclotron with proton beam energy not adjustable to lower than 13 MeV is difficult to be used for the 64Ni target based 64Cu production due to the need for a larger amount of 64Ni target and a special target design
Trang 2In contrast, the 68Zn target based production route
was developed more than 10 years ago.15–18 This
process was based on the 68Zn(p,αn)64Cu reaction and
performed by separating 64Cu from the “waste” solution
of the 68Zn(p,2n)67Ga reaction based 67Ga production
process This production route seems more economic in
the target utilization, because both 67Ga and 64Cu can be
produced from the same low cost target However, the
different side nuclear reactions inducing several
longer-lived radionuclides in the 68Zn target and its substrate
are the main disadvantages Besides, the potential of
67Ga contamination in 64Cu is high due to the much
higher reaction yield and much longer half-life of the
67Ga radionuclide The 68Zn(p,2p)67Cu reaction induced
67Cu and the target substrate contaminated “cold” Cu
elemental impurity in the 64Cu product are crucial
problems in performing the 68Zn target based production
route So, the effective target design, optimal proton
beam energy utilization and good radiochemical
separation should be the main issues concerned about
regarding the 68Zn target based 64Cu production As for
the quality assessment the analysis of the overlapping
gamma-ray spectra should be developed to identify 67Ga
and 67Cu radionuclide contaminations in the 68Zn target
based 64Cu product The lack of an analysis method for
the evaluation of 67Ga and 67Cu radionuclide
contamination may create a pitfall that fails to draw
one’s attention on the performance of the 67Ga-64,67Cu
separation
Above are the reasons why the 68Zn target based
64Cu production and its quality assessment are worthy of
further investigation In this paper some important
aspects regarding the 68Zn target based 64Cu +67Ga
production technology and the quality of the 64Cu
product are reported
Experimental
Reagent and material
The commercially available anion-exchange resin
AG1-X4 and cation-exchange resin AG50W-X4
(Bio-Rad) with average particle size of 200–400 mesh were
used for the radiochemical separations Analytical grade
hydrochloric acid and Milli-Q purified water were used
for the whole experimental process Isotopically
enriched 68Zn target was purchased from Trace-Sciences
International Inc USA.27 The target isotopic
compositions were 68Zn (>99.4%), 67Zn (0.43%), 66Zn
(0.08%), 64Zn (<0.01%), 70Zn (0.09%) and other
chemical impurities (<10 ppm)
Apparatus, radioactivity and radionuclide calibration
The radioactivity of the different radioisotopes was
Radioactivity measurement and radionuclide identification were carried out using an Ortec gamma-ray spectrometer coupled with a high purity Ge detector The gamma-ray energy and radioactivity calibration of this analyser system was performed using a 152Eu radioisotope solution standard The chromatographic elution profile was recorded on-line during the radionuclide separation process using a HPLC radioisotope detector coupled with the LAURA software supported computer-radioactive counter system
The targetry and the cyclotron proton bombardment of the 68 Zn target
The Ni–Cu (substrate)–68Zn target system, which is routinely used for the 67Ga radioisotope production, was applied in co-operation with the radioisotope production unit of the National Medical Cyclotron (NMC) Australia The target system was prepared by plating the metallic 68Zn onto a Ni coated Cu substrate The surface area of 68Zn target was 9.2854 cm2 and the Cu substrate surface (33.5 cm2) was coated with approximate 780 mg
Ni Approximately 800 mg 68Zn was used for each proton bombardment with the 29 MeV protons
Radiochemical separation of radionuclides from the cyclotron irradiated 68 Zn target and the 64 Cu radioisotope product
A glass column of 1.0 cm in diameter × 15 cm length loaded with anion exchange resin AG1-X4 was used for the chromatographic separation of different radionuclides (64Cu, 67Cu, 67Ga, 56Ni, 57Ni, 55Co, 56Co,
57Co, 65Zn, 68Zn) from the 68Zn target solution from which the majority of 67Ga radionuclide was removed during the 67Ga production process The 67Ga separation from the 68Zn target solution was carried out by retaining 67Ga in a cation-exchange resin AG50W-X4 and eluting all other radionuclide and 68Zn with 8M HCl solution.18
The anion-exchange resin column loading was performed as follows: The required amount of AG1-X4 resin was soaked in 0.1M HCl solution in a glass vial Then the degassing of resin was performed by shaking the vial in an ultra-sonic water bath for 5 minutes with vacuum application The degassed resin was then packed into the above mentioned glass column A peristaltic pump applied on the out-let of the column was used to draw eluent through the column After flushing with 6M HCl solution and reconditioning with HCl solution of relevant concentration, the column was ready to use for chromatographic separation
The 67Ga-pre-eliminated 68Zn target solution, as mentioned above, was added with some drops of H2O2 (30%), boiled for 5 minutes and cooled to room
Trang 3resin column The separation process was performed
with successive isocratic elution and/or concentration
gradient elution Samples were also taken from each
elution fraction for the gamma spectrometric evaluation
The overlapped gamma-ray spectrum analysis
and its application for the assessment
of 67 Cu and 67 Ga radionuclide content
The overlapped gamma-ray spectrum of the mixture
of two radioisotopes A and B is depicted in Fig 1
(a) Gamma-ray peak area:
0
,γ
A
S = partial area of photo-peak E0 belonging to
radionuclide A;
0
,γ
B
S = partial area of photo-peak E0 belonging to
radionuclide B;
0
γ
S =S A,γ0+S B,γ0: total area of photo-peak E0
1
,γ
A
S = partial area of photo-peak E1 belonging to
radionuclide A;
1
,γ
B
S = partial area of photo-peak E1 belonging to
radionuclide B;
1
γ
S =S A,γ1+S B,γ1: total area of photo-peak E1
1
, n
A
S γ = partial area of photo-peak En belonging to
radionuclide A;
1
, n
B
S γ = partial area of photo-peak En belonging to
radionuclide B;
n
Sγ =S A,γn1+S B,γn1: total area of photo-peak En
(b) Relative intensity ratio of gamma-rays
For radionuclide A:
The corrected count numbers calculated from the gamma-peak area and its counting efficiencies,
n f f f
fγ0, γ1, γ2, , γ (%), are the following:
0
0 100
, 0
γ
γ
f
S
1
1 100
, 1 γ
γ
f
S
n
n f
S
A n A
γ
γ 100
, ⋅
was set up as follows:
From the definition of gamma-ray absolute intensity
of the nuclide A, I A,γ (%), it is deducible that:
0
1
,
, 0
1
γ
γ
A
A I
I
A A =
By giving
0
1
,
, 0 / 1
γ
γ
A
A I
I
the following is deduced: a1/0.A0=A1
Trang 4The relative intensity ratio a n/0, intensity of the
photo-peak E n versus intensity of the photo-peak E0,
was set up in the same manner as above:
0
,
,
γ
A
A n I
I A
=
By giving
0
,
, 0 /
γ
γ
A
A
I
the following is deduced: a n/0 A0=A n
For radionuclide B:
The corrected count numbers calculated from the
gamma peak area and its counting efficiencies,
n f f
f
fγ0, γ1, γ2, , γ (%), are the following:
0
0 100
,
0
γ
γ
f
S
1
1 100
,
1
γ
γ
f
S
n
n
f
S
γ
γ 100
, ⋅
In the same manner as for radionuclide A the
following ratios are deduced from the gamma-ray
absolute intensity of the nuclide B, I B,γ (%):
photo-peak E1 versus intensity of the photo-peak E0, is:
0 / 1 ,
, 0
1
0
I
I B
B
B
B
=
=
γ
γ
photo-peak E n versus intensity of the photo-peak E0, is:
0 / ,
,
0 B 0 n
B
I
I B
=
=
γ
γ
or b n/0 B0=B n
As experienced in our previous work, the gamma-ray
measurement of a rather weakly radioactivity sample is
increases with the growing-up of the background counts beneath the photo-peak To reduce the calculation error and achieve the lower detection limits, the gamma-ray
of the input data for the calculation process is shown in Table 1
(c) Formulation of the overlapped gamma-ray spectrum analysis for the mixture of two radionuclides A and B
At the photo-peak E0:
photo-peak area Sγ0 as follows (see Sections a and d):
0 0
0 0 0
0 0
0
γ
γ γ
γ γ
γ
f
S f
S f
S
+
⋅
=
⋅
=
At the photo-peak E1:
Total corrected count numbers N1 is calculated from photo-peak area S as follows (see the Sections a and γ1
d):
1 1
1 1 1
1 1
1
γ
γ γ
γ γ
γ
f
S f
S f
S
+
⋅
=
⋅
=
By introducing the relative intensity ratios a1/0 and
b1/0into this equation (see Section d), it leads to:
N1 = a1/0.A0+b1/0.B0 (2)
Table 1 Input database for the overlapped gamma-ray spectrum analysis
Gamma-ray and energy E0, keV E1, keV E2, keV E3, keV … E n, keV
Absolute gamma-ray intensity, I A,γn for nuclide A, % I A,γ0 I A,γ1 I A,γ2 I A,γ3 I A,γn
Absolute gamma-ray intensity,
n B
I ,γ for nuclide B, %
0
, γ
B
I
1
, γ
B
I
2
, γ
B
I
3
, γ
B
I
n B
I ,γ
Gamma-intensity ratio, a n/0 for nuclide A a1/0 a2/0 a3/0 a n/0
Gamma-intensity ratio, b n/0 for nuclide B b1/0 b2/0 b3/0 b n/0
Gamma-counting efficiency,
n
fγ , %
0 γ
Gamma-peak area,
n
Sγ for the counting time t counting, counts
0 γ
S
1 γ
S
2 γ
S
3 γ
S
n
Sγ
Trang 5By putting B0 from Eq (1) into Eq (2) we have the
following:
N1 = a1/0.A0+b1/0.N0–b1/0.A0
0
1 b N (a b ) A
N
⎠
⎞
⎜⎜
⎝
⎛
−
By dividing both sides of this equation with b1/0 and
rearranging, we have the corrected count numbers A0
belonging to the radionuclide A as follows:
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⋅
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⋅
=
1 1
0 / 1
0 / 1
0 0
/ 1 0 1
0
b a
N b
N
N
By introducing the photo-peak area to the A0
calculation, we have the following:
→
⎟⎟
⎞
⎜⎜
⎛
−
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⋅
⎟⎟
⎞
⎜⎜
⎛
−
⋅
=
⋅
=
1
100 1
] / 100
[
] / 100
[
1
1 100
0 / 1
0 / 1
0 / 1
0 / 1
0 / 1
0 0
/ 1 0
1 ,
0
0 0 0
0
1 1
0
0
b a
f
S f
b
S
f S
b a
N b
N N f
S
γ
γ γ
γ
γ γ
γ
γ
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
1
100 1
] [
] [
0 / 1
0 / 1
0 / 1
0 1
0
0 1
b a
f
S b
f
S
f S
γ γ
γ
γ γ
(counts) (3b)
The radioactivity of radionuclide A calculated from
follows:
(Bq) 1
100
100 1
] [
] [
100
0 0 0 1
0
0 1
0
, 0
/ 1
0 / 1
0 / 1
,
0 1 0 ,
t I b
a
f
S b
f
S
f S
t I
A R
A
A A
⋅
⋅
⎟⎟
⎞
⎜⎜
⎛
−
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
⋅
⋅
=
↔
γ γ
γ γ
γ
γ γ
γ
(3c)
where t is the counting time in seconds
radioactivity of radionuclide A in the mixture:
(Bq) 1
100
100 1
] [
] [
100
0 0 0 0
0
0
, 0
/
0 /
0 /
,
0 0
,
t I b
a
f
S b
f S
f S
t I
A R
A n
n n
A n A
n n
⋅
⋅
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
⋅
⋅
=
↔
γ γ
γ γ
γ
γ γ
γ
(3d)
value [Eq (1)] as follows:
) (
1 1
0 / 1 0 / 1
1 0 / 1 0
0 / 1
0 / 1
0 0
/ 1 0 1 0
0 0 0
b a
N a N
b a
N b
N
N N
A N B
−
−
⋅
=
=
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⋅
⎟⎟
⎞
⎜⎜
⎛
−
⋅
−
=
−
=
value as follows:
⎟⎟
⎞
⎜⎜
⎛
−
⋅
⎟⎟
⎞
⎜⎜
⎛
−
⋅
=
1 1
0 / 1
0 / 1
0 0
/ 1 0 1 0
a b
N a
N
N
calculation, we have the following:
→
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
⎟⎟
⎞
⎜⎜
⎛
−
⋅
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⋅
=
⋅
=
1
100 1
] / 100 [
] / 100 [
1
1 100
0 / 1
0 / 1
0 / 1
0 / 1
0 / 1
0 0
/ 1 0
1 ,
0
0 0 0
0
1 1
0 0
a b
f
S f
a S
f S
a b
N a
N N f
S
γ
γ γ
γ
γ γ
γ γ
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
1
100 1
] [
] [
0 / 1
0 / 1
0 / 1
0 1
0
0 1
a b
f
S a
f S
f S
γ γ
γ
γ γ
(counts) (4b)
The radioactivity of radionuclide B calculated from
follows:
Trang 6
(Bq) 1
100
100 1
] [
] [
100
0 0 0 1
0
0
1
0
, 0
/ 1
0 / 1
0 / 1
,
0 1 0 ,
t I a
b
f
S a
f
S
f
S
t I
B R
B
B B
⋅
⋅
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
⋅
⋅
=
↔
γ γ
γ γ
γ
γ
γ
γ
(4c)
where t is the counting time in seconds
radioactivity of radionuclide B in the mixture:
(Bq) 1
100
100 1
] [
] [
100
0 0 0 0
0
0
, 0
/
0 /
0 /
,
0 0
,
t I a
b
f
S a
f
S
f
S
t I
B R
B n
n n
B n B
n
n
⋅
⋅
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
⋅
⋅
=
↔
γ γ
γ γ
γ
γ
γ
γ
(4d)
The mean values R A and R B of all these calculation
results are the actual radioactivity values of
radionuclides A an B in the mixture, respectively
Radioactivity of radionuclide A:
(Bq) )
1 (
100 )
100 (
) 1 ] [
] [
(
1
0 /
0 /
0 /
1 0 ,
0 0 0 0
0
∑
∑
⋅
⋅
−
⋅
⋅
⋅
−
⋅
⋅
⋅
=
=
=
↔
n
A n
n n
n
n A A
t I b
a
f
S b
f
S
f S
n
n
R R
n n
γ γ
γ γ
γ
γ
Radioactivity of radionuclide B:
(Bq) 1
100
100 1
] [
] [
1
1
, 0
/
0 /
0 /
1 0 ,
0 0 0 0
0
∑
∑
⋅
⋅
⎟⎟
⎞
⎜⎜
⎛
−
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
=
↔
n
B n
n n
n
n B B
t I a
b
f
S a
f S
f S
n
n
R R
n n
γ γ
γ γ
γ
γ
Gamma spectrometric measurement and the overlapping
gamma-ray spectrum analysis for the assessment of
67 Cu and 67 Ga in the 64 Cu solution
The above equations will be applied with the
following harmonizations:
nuclide
For 67Ga radioisotope:
gamma-ray photo-peak [Eq (3d)]:
(Bq) 1
100
100 1
] [
] [
0 0 0 0
0
, 67 0
/
0 /
0 /
0 , 67
t I
b a
f
S b
f S
f S
R
Ga n
n n
n Ga
n n
⋅
⋅
⎟⎟
⎞
⎜⎜
⎛
−
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
−
↔
−
γ γ
γ γ
γ
γ γ
(7)
393 keV [Eq (5)]:
(Bq) 1
100
100 1
] [
] [
3 1
3
3 1
, 67 -Ga 0
/
0 /
0 /
3 1 0 , 67 -Ga 67
-Ga
0 0 0 0
0
∑
∑
=
=
=
⋅
⋅
⎟⎟
⎞
⎜⎜
⎛
−
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
=
n
n
n n n
n
n
n
t I
b a
f
S b
f S
f S
R R
n n
γ γ
γ γ
γ
γ
For 67Cu radioisotope:
gamma-ray photo-peak [Eq (4d)]:
(Bq) 1
100
100 1
] [
] [
0 0 0 0
0
, 67 -Cu 0
/
0 /
0 /
0 , 67 -Cu
t I
a b
f
S a
f S
f S
R
n n n
n
n n
⋅
⋅
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛
−
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
↔
γ γ
γ γ
γ
γ γ
(9)
393.0 keV, [Eq (6)]:
(Bq) 1
100
100 1
] [
] [
3 1
3
3 1
, 67 -Cu 0
/ 0 /
0 /
3 1 0 , 67 -Cu 67
-Cu
0 0 0 0
0
∑
∑
=
=
=
⋅
⋅
⎟⎟
⎞
⎜⎜
⎛
−
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛ ⋅
⋅
⎟
⎟
⎠
⎞
⎜
⎜
⎝
⎛
−
⋅
⋅
⋅
=
=
=
n n
n n n
n n
n
t I
a b
f
S a
f S
f S
R R
n n
γ γ
γ γ
γ γ
Trang 7Results and discussion
Radiochemical separation
For the purpose of identify the radioisotopes present
in the 68Zn target solution, the solution sample (67
Ga-pre-eliminated 68Zn target solution), which comes from
the 67Ga production process, was left to decay for 3 days
and then chromatographic separation was performed
The typical separation profiles and the radioisotopes
(64Cu, 67Cu, 66Ga, 67Ga, 56Ni, 57Ni, 55Co, 56Co, 57Co,
65+68 Zn) identified for the relevant chromatographic
fractions were shown in Figs 2 and 3 The good
separations can be achieved using both successive
isocratic elution and a concentration gradient Although
67Ga has been removed from the 68Zn target solution in
the 67Ga production process, a significant amount of
67Ga can be found and further separated from this
post-67Ga-production solution Due to the identical
gamma-ray spectrum of 67Ga and 67Cu, the result of gamma-ray
spectrometric analysis of 67Cu content in the 68Zn target
and/or 64Cu solution could be wrong without the support
of the chromatographic separation Obviously the
chromatographic separation combined with the
overlapped gamma-ray spectrum analysis described in
the next section offers a secure way to evaluate the 67Ga
and 67Cu content in both the target and final 64Cu
product
As for the separation performance, the advantage of
this anion-exchange chromatographic technique is that
the column loading can be performed with post 67 Ga-production target solution of high HCl concentration (8M HCl) and the following elution of the different nuclides can be performed with HCl solutions of lower concentration This avoided the time consumption and corrosive evaporation step involved in the separation process using the organic solvent eluents.18 Besides, the HCl concentration gradient elution, as shown in Fig 3, offers a better chance of automating of the high radioactivity separation which is definitely important for large scale radioisotope production The gamma-ray spectrometric analysis (Fig 4) of the Cu radioisotope fraction collected from the chromatographic separation present in Figs 2 and 3 has shown no contamination of 66+67Ga, 56+57Ni, 55+56+57Co and 65+68 Zn The 67Cu contamination in the 64Cu product, as shown in Fig 4, cannot be definitely removed by any chemical separation method and the issue is discussed in the following section of the proton bombardment optimization
The 66+67Ga fraction clearly separated from the 64+67Cu fraction strongly supported the overlapped spectrum analysis for accurate identification of the 67Cu and 67Ga contents in the less 67Ga contaminated 68Zn target solution used for the 64Cu production and that in the final 64Cu product The 65Zn fraction separation was useful for monitoring the elemental Cu leakage from the
Cu substrate, so that the intactness of the protective Ni interlayer between the 68Zn layer and Cu substrate (Fig 6) could be justified
Fig 2 Chromatographic diagram of the 68 Zn target solution separation using a successive isocratic elution technique
Column: A glass column of 1.0 cm in diameter × 15 cm length loaded with anion-exchange resin AG1-X4
Successive elutions: 5M HCl (0–65 ml) → 3M HCl (65–85 ml) → 2.5M HCl (85–110 ml) → H2O (110–150 ml)
Trang 8Fig 3 Chromatographic diagram of the 68 Zn target solution separation using a concentration gradient elution technique (a) and HCl concentration gradient (b) Chromatographic column: A glass column of 1.0 cm in diameter × 15 cm length loaded
with anion-exchange resin AG1-X4
Fig 4 Gamma-ray spectrum of 64 Cu and 67 Cu radioisotopes in the 64 Cu product ( 64+67 Cu radioisotope elution fraction shown in Fig 2)
Trang 9Fig 5 Gamma-ray spectrum of the different nuclides in the 68 Zn target solution
Table 2 Radionuclides and radioactivity induced in the Ni–Cu (substrate)–68 Zn target system used at NMC
The reactions of threshold energy E Threshold <22.8 MeV were selected for the natural Ni, E Threshold<16 MeV for the
natural Cu and E Threshold<29 MeV for 68 Zn Only radionuclides with the half-life longer than 3 hours were listed
Target RI Half-life Reaction Q-value,MeV E ThresholdMeV , EMeV Max, σMax,
mb
T.T.Y,*
µCi/µAh
68 Zn 67 Ga 78.3 h 68 Zn(p,2n) 67 Ga –11.981 12.158 21 700 8108.0
68 Zn 66 Ga 9.4 h 68 Zn(p,3n) 66 Ga –23.207 23.552 34 235 1800.0
68 Zn 64 Cu 12.7 h 68 Zn(p,αn) 64 Cu –7.790 7.905 30 20 946.0
68 Zn 67 Cu 58.6 h 68 Zn(p,2p) 67 Cu –9.977 10.125 45 3.5 6.7 Nat Ni 56 Ni 6.0 d 58 Ni(p,p2n) 56 Ni –22.466 22.857 42 21 –
Nat Ni 57 Ni 37 h 58 Ni(p,pn) 57 Ni –12.217 12.429 26 260 96
Nat Ni 55 Co 18 h 58 Ni(p,α) 55 Co
60 Ni(p,α2n) 55 Co
–1.336 –21.723
1.359 22.088
16
45
40
14
440 – Nat Ni 56 Co 77 d 58 Ni(p,2pn) 56 Co
60 Ni(p,αn) 56 Co
–19.548 –11.639
19.888 11.835
40
28
350
72
0.0176 – Nat Ni 57 Co 270 d 58 Ni(p,2p) 57 Co
60 Ni(p,α) 57 Co
–8.172 –0.263
8.314 0.268
22
51
540
200
8.8 – Nat Ni 58 Co 71 d 60 Ni(p,2pn) 58 Co
61 Ni(p,α) 58 Co
–19.986 –0.489
20.332 0.000
40
15
180
100
0.22 – Nat Ni 61 Cu 3.3 h 61 Ni(p,n) 61 Cu –3.019 3.069 9.5 480 200
Nat Ni 64 Cu 12.7 h 64 Ni(p,n) 64 Cu –2.457 2.496 11 670 200
Nat Cu 65 Zn 243.8 d 65 Cu(p,n) 65 Zn –2.134 2.167 10.5 230 23
Nat Cu 62 Zn 9.3 h 63 Cu(p,2n) 62 Zn –13.261 13.474 23.4 66 27
Nat Cu 64 Cu 12.7 h 65 Cu(p,pn) 64 Cu –9.910 10.064 26 93 10
Nat Cu 61 Cu 3.3 h 63 Cu(p,p2n) 61 Cu –19.738 20.054 35 149 40
* T.T.Y: Thick target yield for the 29 MeV proton bombardment
Trang 10Quality assessment, targetry development and
proton-bombardment optimization for the improvement
of the 64 Cu and 67 Ga simultaneous production process
The gamma-ray spectrum analysis results of the 68Zn
target solution (Fig 5) and that of the
chromato-graphically separated elution fractions (Figs 2 and 3)
showed the presence of different radionuclides which
were induced by several nuclear reactions between the
through-penetrated protons and the different components
of the target assembly The radionuclides induced in the
Ni–Cu (substrate)–68Zn target system shown in Fig 6
and Table 2 have a good agreement with the results
obtained from gamma-ray spectrum analysis and
radiochemical separation
The 68Zn targetry was based on the solid target
assembly currently used at NMC The target surface
tilted at 6° with respect to the beam axis resulting in an
enlargement of the axial beam by a factor of 9.6 and a
corresponding reduction in material thickness
This target contained approximate 800 mg 68Zn The
thickness of 68Zn layer was 120.66 µm This offers the
1154.5 µm effective thickness of the 6° angle tilted
target This effective thickness is relevant to the
stopping power of the 29 MeV→17 MeV proton energy
range in the metallic 68Zn target
The thickness of the Ni layer underneath the 68Zn
was 26.2 µm, giving the 250.0 µm effective thickness in
this target assembly This effective thickness is relevant
to the stopping power of the 17 MeV→12 MeV proton
energy range in the metallic nickel
The characteristics of nuclear reactions induced in the Ni–Cu (substrate)–68Zn target system and their excitation functions were calculated (if not found in the literatures) and collected from the References 10, 14, 23,
29, 32 and presented in Table 2 and Figs 6 and 7 The reaction yields in Fig 8 were calculated based on the excitation function in Fig 7 and the stopping power was calculated using the data and equations in the literature.30,31
Obviously the current 68Zn target was designed for
67Ga production only As seen in Tables 2, 3 and 4, the
67Ga product was also contaminated with a significant
66Ga amount at E.O.B Because the half-life of 66Ga
(T1/2=9.4 hours) is shorter than that of 67Ga (T1/2=78.3 hours), the 66Ga contamination can be removed by standing the 67Ga product for the 66Ga decay Around
74 hours cooling time is required to decrease the 66Ga activity to the level of less than 0.2% (compared to the
67Ga radioactivity) as required by the British Pharmacopeia.33 However, this process causes the loss
of nearly 50% of the 67Ga activity too (compared to that
at E.O.B), which affects the production economics The applied proton energy range (17–29 MeV) is required to give a reasonably high yield of 67Ga from a productivity point of view However, the high radioactivity of the side reaction induced 66Ga, 67Cu, 56+57Ni, 55+56+57Co and 65+68Zn radionuclides was a problem for the radiochemical separation and radiation protection during the target disassembling and processing
Fig 6 The target assembly cross section and the radionuclides induced in the target currently used for the 67 Ga and 64 Cu production at NMC The
68 Zn, Nat Ni and Nat Cu layers were of 120.66 µm, 26.2 µm and 4.5 mm, respectively The stopping power and range of proton were calculated using
the data and equations in the literature 30,31