trs 398 code of practice for heavy ion

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TRS 398 CODE OF PRACTICE FOR HEAVY ION BEAMS

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Page 1: Trs 398 code of practice for heavy ion

TRS 398

CODE OF PRACTICE FOR HEAVY

ION BEAMS

Page 2: Trs 398 code of practice for heavy ion

This Code of Practice is based on a

calibration factor in terms of absorbed dose

to water of an ionization chamber in a

reference beam which is taken to be 60Co

gamma rays.

The Code of Practice applies to heavy

ion beams with atomic numbers between

2(He) and 18(Ar) which have ranges of 2–

30 g/cm2 in water.

The depth dose distribution of a mono

energetic heavy ion beam in water is shown

in figure

Introduction

Page 3: Trs 398 code of practice for heavy ion

For clinical applications of heavy ion beams

we have to generate ‘spread-out Bragg peaks

‘(SOBP) in order to include the complete

target volume inside the SOBP.

In clinical applications it is common to use

a biological effective dose instead of a physical

dose (absorbed dose to water) because of the

uniformity in its dose distributions.

The difference between the two kinds of

distributions can be compared from the figures

. In the physical dose distribution we can see a

lack of uniformity in the SOBP.

The use of a biological effective dose makes

it possible to compare results obtained with

conventional radiotherapy to those using heavy

ion radiotherapy.

Page 4: Trs 398 code of practice for heavy ion

Unlike the clinical applications ,the dosimetry of heavy ion is carried out by

determination of the physical dose using an ionization chamber calibrated in terms

of absorbed dose to water, ND,w,Qo.

The goal behind this approach is to achieve international consistency in

dosimetry by adopting the same formalism and procedures for all the radiotherapy

beams used throughout the world.

Unfortunately, Task Group 20 in 1984 by the Association of American Physicists

in Medicine is the only protocol available regarding dosimetry recommendations .

Thus there is a need for a new protocol which will be able to establish a global

consistency in the determination of absorbed dose to water with heavy ions and is

common to dosimetry protocols.

For an accurate determination of absorbed dose using an ionization chamber, we

need to know the energy spectra of the incident heavy ion beam, the projectile

fragments as well as that of the target fragmented nuclei.

Page 5: Trs 398 code of practice for heavy ion

Dosimetry equipments

Ionization chambers

Cylindrical and plane-parallel ionization chambers are recommended for use as

reference instruments in clinical heavy ion beams.

cylindrical ionization chambers are preferred for reference dosimetry for SOBP

width ≥ 2.0 g/cm2 and plane-parallel chambers are preferred for SOBP width < 2.0

g/cm2.

The reason for this preferences is the higher combined standard uncertainty on

Dw,Q for plane-parallel ionization chambers due to their higher uncertainty for pwall

in the 60Co reference beam quality.

In the case of cylindrical chambers ,graphite walled are preferred to plastic

walled chambers because of their better long term stability and smaller chamber to

chamber variations.

Page 6: Trs 398 code of practice for heavy ion

Since the depth dose distribution in the SOBP for heavy ion beams is not flat and

the slope depends on the width of the SOBP , measurement of an effective point of

the chamber, Peff, is important.

The reference point of the cylindrical chamber should be positioned at a distance

0.75 rcyl deeper than the point of interest in the phantom, where rcyl is the inner

radius of the chamber.

For plane-parallel ionization chambers, the reference point is taken to be on the

inner surface of the entrance window, at the centre of the window. This point is

positioned at the point of interest in the phantom.

The cavity diameter of the plane-parallel ionization chamber or the cavity length

of the cylindrical ionization chamber should not be larger than approximately half

the reference field size.

Page 7: Trs 398 code of practice for heavy ion

Phantoms and chamber sleeves

Water is recommended as the reference medium for measurements of absorbed

dose.

The extension of phantom should be at least 5 cm beyond all four sides of the

field size at the depth of measurement and should extend to at least 5 g/cm2

beyond the maximum depth of measurement.

In horizontal beams, phantom should have plastic window with a thickness twin

between 0.2 and 0.5 cm. In the case of non-waterproof chambers, a waterproofing

sleeve made of PMMA, with a thickness than 1.0 mm have to be used.

To provide equilibrium air pressure in the chamber ,the air gap between the

chamber wall and the waterproofing sleeve should be within (0.1–0.3 mm).

Page 8: Trs 398 code of practice for heavy ion

If it is possible, the same waterproofing sleeve that was used for calibration of user

chamber should also be used for reference dosimetry. Otherwise another sleeve of

the same material and of similar thickness should be used.

Use of plastic phantoms for reference dosimetry in heavy ion beams is not

recommended.

One of the reason for this is difficulty in availability of water to plastic fluence

correction factors, hpl, and other reason is difference in the fluence of heavy ions

including fragmented particles in a plastic phantom and that in a water phantom.

However, for routine quality assurance measurements plastic phantoms can be

used, provided a transfer factor between plastic and water has been established.

Page 9: Trs 398 code of practice for heavy ion

BEAM QUALITY SPECIFICATION

Unavailability of both experimental and theoretical data regarding spectral

distributions of heavy ion beams makes beam quality specification more

impractical.

The current practice for characterizing a heavy ion beam is to use the atomic

number, mass number, energy of the incident heavy ion beam, width of SOBP and

range.

DETERMINATION OF ABSORBED DOSE TO WATER

From the spread out Bragg peak of a heavy ion figure we have seen that

The depth dose distribution is not flat, and the dose at the distal end of the SOBP

is smaller than that at the proximal part.

The slope near the centre of a broad SOBP is rather small whereas that of a

narrow SOBP is steep.

The reference depth for calibration should be taken at the centre of the SOBP, at

the centre of the target volume.

Reference conditions for the determination of absorbed dose to water are given as

Page 10: Trs 398 code of practice for heavy ion
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Determination of absorbed dose under reference conditions

The absorbed dose to water at the reference depth zref in water in a heavy ion beam

of quality Q and in the absence of the chamber is given by

where MQ is the meter reading of the dosimeter in accordance with the

reference conditions corrected for the influence quantities like

temperature and pressure, electrometer calibration, polarity effect

and ion recombination etc

ND,w,Qo is the calibration factor in terms of absorbed dose to water for the

dosimeter at the reference quality Qo.

kQ,Qo is a chamber specific factor which corrects for differences between

the reference beam quality Qo and the actual beam quality being

used, Q

Page 12: Trs 398 code of practice for heavy ion

Recombination correction in heavy ion beams

Dose rate will be very high when beams are generated by pulsed scanning

techniques and so recombination effects must be taken into account.

The correction factor for general (Volume) recombination is obtained

experimentally by the two voltage method.

When general recombination is negligible, initial recombination should be taken

into account for heavy ion beams, especially when the dose is measured using

plane-parallel ionization chambers.

The collected ionization current should be fitted by the linear relation

l/icol = 1/i∞ + b/V

where V is the polarizing voltage applied to the chamber. The correction factor is

given by ksini = i∞ /icol.

Page 13: Trs 398 code of practice for heavy ion

Part of worksheet regarding calculation for Initial ion recombination

Page 14: Trs 398 code of practice for heavy ion

Values of kQ,Qo

Beam quality specifications are not currently used for the dosimetry of heavy-ion

beams and so kQ values depend only on the chamber type used.

Experimental values of the factor kQ,Qo are not readily available and, therefore, in

this report only theoretical values will be used.

The correction factor is defined as.

Since there is no primary standard of absorbed dose to water for heavy ion

beams is available, all values for kQ,Qo given in this Code of Practice are derived by

calculation and are based on 60Co gamma radiation as the reference beam quality Qo

at 60Co.

Page 15: Trs 398 code of practice for heavy ion

There is no information available on perturbation factors for ion chambers in

heavy ion beams, and so is assumed as unity.

The stopping-power ratios and W values for heavy ion beams are taken to be

independent of the beam quality, because of lack of experimental data.

The contribution of fragmented nuclei to stopping-power ratios and W values

are also assumed to be negligible.

Constant values of the stopping-power ratio and W value are therefore

adopted here for all heavy ion beams — these are 1.130 and 34.50 eV,

respectively.

As the stopping power ratio sw,air of heavy ions is so close to that of 60Co, the

kQ values for heavy ions are dominated by the ratio of Wair values and the

chamber specific perturbation factors

Page 16: Trs 398 code of practice for heavy ion

Values of kQ for various cylindrical and plane-parallel ionization chambers

in common use are given. Some of the chambers listed in this table fail to

meet some of the minimum requirements .However, they have been

included because of their current clinical use.

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