Highlights
- •Lack of primary standards for small fields.
- •Dose Area Product (DAP) is used to overcome the point dose traceability breakdown.
- •Primary standards in terms of DAP are established down to 5 mm field size.
- •Promising approach to surrogate the absorbed dose at a point in small fields.
Abstract
Purpose
Methods
Results
Conclusions
Keywords
1. Introduction
- -A clear reduction in the dispersion of results obtained with different detectors has been shown by applying the IAEA TRS 483 correction factors [14,15]. However, dispersions on the OF up to 5 % have been reported [[16]] and confirmed by a larger scale study [[15]]. Therefore, the use of several detectors with their associated correction factors does not allow the determination of a unique OF. In all cases, IAEA TRS 483 and the recent AAPM TG 155 report [[17]] recommend using at least two detectors and comparing the results.
- Das I.J.
- Francescon P.
- Moran J.M.
- Ahnesjö A.
- Aspradakis M.M.
- Cheng C.-W.
- et al.
Report of AAPM Task Group 155: Megavoltage photon beam dosimetry in small fields and non-equilibrium conditions.Med Phys. 2021; 48https://doi.org/10.1002/mp.v48.1010.1002/mp.15030 - -IAEA TRS 483 correction factors were determined from data up to 2015. For PTW 60019 microdiamond detector, correction factors to be applied for fields smaller than 1 × 1 cm2 is still subject to debate in the medical physics community [[18]].
- -New detectors for small fields measurements arrived on the market [19,20,21] and sometimes replace an existing model tabulated in the IAEA TRS 483. The use of these new detectors for OF is conditional on the knowledge of the associated correction factors. But as pointed out by the authors of the IAEA TRS 483, ‘users adopting new specific datasets appearing in the literature should be aware of the risks they assume’ [[22]]. The same issue appears for recent and future machines not tabulated in the code of practice.
2. Material and methods
2.1 Formalism
where:
- -Dcore/Mon is the average absorbed dose in the core (sensitive part) of the large section calorimeter normalized to the monitor ionization chamber;
- -Q*w/Mon is the charge measured by the reference ionization chamber corrected for polarization and recombination effects normalized to the monitor ionization chamber. The integration area being a critical quantity of the DAP, a 2D dose integral correction kint is introduced to take into account the difference in the deposited energy measured between the core and the collection area of the plane-parallel ionization chamber, related to their possible area differences (see Section 2.5.2). The corrected charge Q*w is then defined as: Q*w = Qw × ks × kpol × kint with Qw the charge measured by the reference ionization chamber in a 30 cm × 30 cm × 30 cm water-filled tank volume (denoted by water phantom afterwards) and corrected for influence quantities: temperature, pressure, humidity;
- -[Dw(Vcore) / Dcore]MC is the graphite to water dose conversion factor calculated by Monte Carlo as the ratio of the average absorbed dose to water in a water volume similar in shape, dimensions and position to the graphite core volume Vcore and the average dose in the core Dcore;
- -Score is the graphite core area (perpendicular to the beam direction);
- -The impurity correction factor ki takes into account the effects on the absorbed dose to the core of all the impurities within the core that are different from graphite (thermistors, resin and kapton). This correction was considered here dosimetrically negligible because thermistors are located at the periphery of the core and are not in the direct beam. So it was taken equal to unity, with an uncertainty of 0.1%.
- 1-Convert DAP into point dose [[37]]. This could be done with films through a volume average correction factor [[38]] using a 2D dose map of the beam. The improvement of performances of film dosimetry [[39]] and dose distribution reconstruction from profiles measured with point dose detectors [[40]] is an active research field and the results obtained will benefit to this approach.
- 2-The best and more direct option to exploit DAP primary standards would be to directly introduce DAP in Treatment Planning Systems (TPS). This would mean a formalism modification in TPS for OF input data, considering an integrated measurement instead of a point dose.
2.2 Methodology


2.3 Graphite calorimetry


2.4 DAP plane-parallel ionization chamber

2.5 Monte Carlo calculations
2.5.1 Graphite to water dose conversion factor
Parameter | Value |
---|---|
Global ECUT (MeV) | 0.512 |
Global PCUT (MeV) | 0.001 |
Brem cross sections | NIST |
Bound Compton scattering | On |
Pair angular sampling | KM |
Rayleigh scattering | On |
Electron Impact Ionization | On |
Photon cross sections | mcdf-xcom |
2.5.2 2D dose integral correction
where g is the 2D dose distribution in water at the reference depth of 10 cm and a source distance of 100 cm, and Score and SDAP are respectively the area of the core and of the effective collection area of the plane-parallel ionization chamber. The diameter of the core can be determined using a mechanical caliper. For the plane-parallel ionization chamber collection diameter, the determination was more challenging and was measured by X-ray tomography.
2.5.3 Monte Carlo modeling of DAP plane-parallel ionization chamber

3. Results and discussion
3.1 DAP plane-parallel ionization chamber performances as a reference detector
Stability under irradiation (%) | Noise contribution to signal (%) | kpol | ks (5 mm) | ks (15 mm) | |
---|---|---|---|---|---|
DAP1 | 0.04 | 0.006 | 0.9992(0) | 1.0016(5) | 1.0034(6) |
DAP2 | 0.05 | 0.008 | 0.9991(1) | 1.0014(5) | 1.0034(5) |
3.2 Calibration coefficients NDAP,w

6 MV FFF – Circular fields | |||||
---|---|---|---|---|---|
Ionization Chamber | DAP1 | DAP2 | |||
Area (mm2) | Field size diameter (mm) | NDAP,w x108 (Gy cm2 C-1) | uc (%) | NDAP,w x108 (Gy cm2 C-1) | uc (%) |
19.6 | 5 | 1.641 | 0.62 | 1.716 | 0.63 |
44.2 | 7.5 | 1.643 | 0.61 | 1.719 | 0.62 |
78.5 | 10 | 1.650 | 0.61 | 1.724 | 0.62 |
132.7 | 13 | 1.655 | 0.61 | 1.726 | 0.62 |
176.7 | 15 | 1.657 | 0.61 | 1.730 | 0.62 |
6 MV FFF – Square fields | |||||
Ionization Chamber | DAP1 | DAP2 | |||
Area (mm2) | Field size side length (mm) | NDAP,w x108 (Gy cm2 C-1) | uc (%) | NDAP,w x108 (Gy cm2 C-1) | uc (%) |
25 | 5 | 1.646 | 0.69 | 1.719 | 0.70 |
49 | 7 | 1.648 | 0.64 | 1.720 | 0.65 |
100 | 10 | 1.657 | 0.64 | 1.729 | 0.65 |
169 | 13 | 1.662 | 0.64 | 1.731 | 0.65 |
225 | 15 | 1.671 | 0.64 | 1.735 | 0.64 |
Value | u (%) | |
---|---|---|
(Dcore/Mon / Qw/Mon) (Gy C-1) | 2.343 107 | 0.20 |
kpol | 0.9985 | 0.03 |
ks | 1.0016 | 0.05 |
kint | 1.0003 | 0.06 |
[Dw (Vcore) / Dcore]MC | 0.9908 | 0.57 |
Score (cm2) | 7.0700 | 0.04 |
ki | 1.0000 | 0.10 |
NDAP,w (Gy cm2 C-1) | 1.641 108 | 0.62 |
3.3 Comparison of calculated dose ratios and measured calibration coefficients NDAP,w

where sw,air is the water-to-air stopping-power ratio. The dose ratios Dw/Dcav increase is thus related to 1- sw,air increase, 2- pch increase, or 3- both. Results showed that sw,air are constant within the statistical uncertainties given by Monte Carlo of about 0.2%. Dose ratios (and in extension calibration coefficients) increase with the field size is then explained solely by the fluence perturbation factor pch which is related to the design geometry of the ionization chamber and the materials used to build it [

4. Conclusion
Funding sources
Declaration of Competing Interest
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